JP3841339B2 - Viscous ground purification structure and purification method - Google Patents

Viscous ground purification structure and purification method Download PDF

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JP3841339B2
JP3841339B2 JP2001384127A JP2001384127A JP3841339B2 JP 3841339 B2 JP3841339 B2 JP 3841339B2 JP 2001384127 A JP2001384127 A JP 2001384127A JP 2001384127 A JP2001384127 A JP 2001384127A JP 3841339 B2 JP3841339 B2 JP 3841339B2
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layer
ground
viscous
ventilation
purification
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JP2003181440A (en
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和昭 日置
健二 原田
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不動建設株式会社
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【0001】
【発明の属する技術分野】
本発明は、粘性土層の下方に通気層を有する粘性質地盤において、地下水位以上の地盤中に存在するガス状の汚染物質を浄化する粘性質地盤浄化構築物および浄化工法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。
【0003】
このような汚染土壌や汚染地下水を浄化する方法としては、従来、汚染地盤区域の周囲に井戸を掘ってポンプで揚水し、この揚水した地下水に溶解した汚染物質を地上のばっ気処理装置や活性炭吸着処理装置で回収する地下水揚水法や、地下水位が低く、該地下水位より上方の地盤に存在するガス状の汚染物質を吸引し地上の活性炭吸着処理装置で汚染物質を回収する土壌ガス吸引法などがある。
【0004】
【発明が解決しようとする課題】
しかしながら、地下水揚水法や土壌ガス吸引法の適用範囲及び浄化効率は地盤条件により大きく左右される。すなわち、地下水揚水法や土壌ガス吸引法は通水性又は通気性の高い砂礫地盤や砂質地盤においては、浄化効率もよく有効な方法であるものの、通水性又は通気性の低い粘性質地盤では、揚水あるいはガス吸引の影響範囲が小さく浄化効率が悪いため処理費用が膨大となったり、適用さえ困難な場合がある。特に、丘のような海抜が高い地盤では、地下水位が地盤の深部にあり、地下水位より上方にガス状の汚染物質が存在することがあり、このままでは当該地盤が例え砂質地盤であっても地下水揚水法は適用できない。
【0005】
従って、本発明の目的は、地下水位より上方の地盤に汚染層が存在する通気性の低い粘性質地盤においても、土壌ガス吸引法の適用が可能で、浄化効率が高く、処理期間の大幅短縮を図ることができる粘性質地盤浄化構築物及び浄化工法を提供することにある。
【0006】
【課題を解決するための手段】
かかる実情において、本発明者らは鋭意検討を行った結果、粘性土層の下方に通気層を有する粘性質地盤で、地下水位が通気層あるいは通気層より下方に位置し且つ該地下水位よりも上方に汚染層が存在する地盤に、通気柱を適宜のピッチで多数造成して地盤の透気性の改善を図り、次いで、ガス吸引装置を稼動させ、吸引孔の通気層部分に配設された吸引ポイントを介して、ガス状の汚染物質を地上に回収する浄化工法を採れば、通気性の低い粘性質地盤においても、土壌ガス吸引法の適用が可能で、浄化効率が高まり、処理期間の大幅短縮を図ることができるため処理コストを低減できることなどを見出し、本発明を完成するに至った。
【0007】
すなわち、本発明(1)は、粘性土層の下方に通気層を有する粘性質地盤で、地下水位が該通気層あるいは該通気層より下方に位置し且つ該地下水位よりも上方に汚染層が存在する地盤を浄化する構築物であって、該粘性土層を貫通し更に該通気層の中まで達する吸引孔と、吸引ポイントを該吸引孔の該通気層部分に配設するガス吸引装置と、該ガス吸引装置の周りに分散配設され、且つ該粘性土層を貫通し少なくとも該通気層まで達する砂杭又は砕石杭と、を備える粘性質地盤浄化構築物を提供するものである。
【0008】
また、本発明(2)は、粘性土層の下方に通気層を有する粘性質地盤で、地下水位が該通気層あるいは該通気層より下方に位置し且つ該地下水位よりも上方に汚染層が存在する地盤に、砂杭又は砕石杭を適宜のピッチで多数造成して粘性土層の透気性の改善を図り、次いで、ガス吸引装置を稼動させ、吸引孔の通気層部分に配設された吸引ポイントを介して、該ガス状の汚染物質を地上に回収する粘性質地盤の浄化工法を提供するものである。
【0009】
本発明によれば、地下水位より上方の地盤に汚染層が存在する通気性の低い粘性質地盤においても、土壌ガス吸引法の適用が可能で、浄化効率が高まり、処理期間の大幅短縮を図ることができるため処理コストを低減できる。
【0010】
【発明の実施の形態】
次に、本発明の実施の形態における粘性質地盤の浄化工法を図1〜図3を参照して説明する。図1は本例の粘性質地盤の浄化構築物を模式的に示す平面図、図2は図1の浄化構築物を模式的に示す断面図、図3は本例の粘性質地盤の浄化工法を説明する図をそれぞれ示す。なお、図3中の矢印はガス状の汚染物質の流れを示す。
【0011】
本実施の形態における粘性質地盤浄化構築物10は、粘性土層1の下方に通気層2を有する粘性質地盤9で、地下水位WLが通気層2あるいは通気層2より下方に位置し且つ該地下水位WLよりも上方に汚染層4が存在する地盤を浄化する構築物である。本発明において、粘性質地盤9は、粘性土層1の下方に通気層2を有する地盤であれば、特に制限されず、粘性質地盤9中に占める粘性土層1及び通気層2の比率に制限されるものではない。すなわち、粘性質地盤9は、粘性土層1の厚みが通気層2の厚みと同等又は通気層2より大きい地盤及び粘性土層1の厚みより通気層2の厚みが大きい地盤のいずれも含むものである。
【0012】
粘性質地盤9は、粘性土層1の下方に通気層2を有する地盤であれば、特に制限されず、粘性土層1の上方には表層部を有していてもよい。粘性土層1は、シルト質、あるいは粘土質といわれる地盤であり、通気層2は砂質土層あるいは砂礫土層といわれる地盤である。また、汚染物質としては、ガス状で存在する揮発性有機塩素化合物などが挙げられる。汚染物質で汚染された汚染層4は、通常、自然地下水位WLより上方の粘性土層1中に存在するが、これに限定されず、例えば、粘性土層1から通気層2に亘って存在していてもよい。
【0013】
吸引孔6は、粘性土層1を貫通し更に通気層2の中まで達するものであり、例えば、中空管などが使用される。吸引孔6の通気層部分61の深さは、ガス吸引装置の吸引ポイント7が設置できる深さがあればよいが、図2に示すように地下水位WLまで達するものでもよい。ガス吸引装置としては、吸引ポイント7が吸引孔6の通気層部分61に配設されるものであれば、特に制限されず、吸引ポイント近傍にポンプ本体を有するもの、あるいはポンプ本体が当該場所になく、吸引ポイント7に接続する吸引配管を通して地上の真空ポンプで吸引するものであってもよい。また、吸引ポイント7の配設場所としては、特に制限されないが、吸引孔6の通気層部分61であって、通気層2の表面近傍とすることが、通気柱5を通じて通気層2に流れる汚染物質を直ちに吸引でき、汚染物質の通気層2内での拡散を防止できる点で好適である。
【0014】
通気柱5は粘性土層1の透気性の改善を図るものであり、吸引ポイント7の周りに分散配設されるものであれば、特に制限されず、通気柱5の深度方向に対しては粘性土層1を貫通し少なくとも通気層2まで達するものである。従って、通気柱5はその下端部が通気層2の表面までのもの、通気層2の途中にあるもの、通気層2を貫通して地下水位WLまで達するもの(図2参照)のいずれも使用できる。このうち、通気柱5の下端部が通気層2の表面までのものが、通気柱5の構成材料を節減でき、施工工期も短縮できる点で好適である。通気柱5としては、砂杭及び砕石杭が使用できる。砂杭及び砕石杭は公知の砂杭造成工法により造成することができる。具体的には、中空管を地盤中の設計深度まで貫入した後、地表まで引き抜く過程で、管内に投入された砂等を排出して砂杭を造成するサンドドレーン工法が適用できる。汚染層4が存在する粘性土層1は、この多数の通気柱5の造成により、通気路が形成されるから、透気性が高められる。このため、粘性土層1に対する土壌ガス吸引法の適用が実用上可能となり、従来困難であった汚染された粘性質地盤に対する浄化効率が高まる。また、砂杭や砕石杭の造成により、粘性土層1の地盤強度を高めることができる。
【0015】
吸引ポイント7の周りに分散配設される通気柱5の打設間隔は、地盤条件及び浄化期間の要求から適宜決定される。すなわち、粘性土層1がシルト質地盤の場合、通気柱5の打設間隔を大きくでき、粘土質地盤の場合、通気柱5の打設間隔は小さくなる。このように、粘性土層の通気性に応じて、通気柱5の打設間隔が適宜決定される。また、浄化期間を長くできる場合には、通気柱5の打設間隔を大きくでき、浄化期間を短くしたい場合には、通気柱5の打設間隔は小さくなる。このように、浄化期間の要求に応じても通気柱5の打設間隔が適宜決定される。
【0016】
本例の粘性質地盤の浄化構築物10においては、汚染層4を囲むように不図示の遮蔽壁が形成されていてもよい。遮蔽壁は汚染層4が存在する浄化対象区域と、それ以外の浄化対象外区域を区画すると共に、汚染物質が浄化対象外区域へ流出することを防止することができる。遮蔽壁としては、特に制限されず、引き抜き可能な鋼矢板が使用できる。遮蔽壁は、例えば、汚染層4が存在する粘性土層1及び通気層2を貫通し、地下水位WLまで達するものが好適である。
【0017】
上記の浄化構築物10を用いて粘性質地盤を浄化する工法を図3を参照して説明する。先ず、地盤条件や汚染状況を把握して、浄化構築物10の大きさなどが決定され、前述の浄化構築物10が構築される。すなわち、粘性土層1の下方に通気層2を有する粘性質地盤9で、地下水位WLが通気層2に位置し且つ該地下水位WLよりも上方に汚染層4が存在する地盤に、通気柱5を適宜のピッチで多数造成して粘性土層1の透気性の改善を図る(図2)。この状態から、ガス吸引装置を稼動させる。
【0018】
汚染層4に存在するガス状の汚染物質は吸引ポイント7の吸引作用で通気柱5に流れ込む(図3中、矢印Xの方向)。次いで、汚染物質を吸引した気流は、通気柱5内を下方に移動し、通気柱5の通気層部51に到達後、同様に、吸引ポイント7の吸引作用で通気層2内を吸引ポイント7方向に流れる(図3中、矢印Yの方向)。次いで、吸引ポイント7から不図示の吸引配管で地表に回収される。この吸引ガス中に含まれる汚染物質は、例えば、活性炭吸着処理装置など公知の地上回収装置で回収される。このような汚染物質の処理は、吸引ガス中の汚染濃度が一定値以下となるまで行われる。
【0019】
このような浄化構築物10を用いた粘性質地盤9の浄化工法によれば、汚染層4が存在する粘性土層1は、この多数の通気柱5の造成により、通気路が形成されるから、透気性が高められる。このため、粘性土層1に対する土壌ガス吸引法の適用が実用上可能となり、従来困難であった汚染された粘性質地盤に対する浄化効率が高まる。
【0020】
【発明の効果】
本発明によれば、地下水位より上方の地盤に汚染層が存在し、該地盤が通気性の低い粘性土層であっても、土壌ガス吸引法の適用が可能で、浄化効率が高まり、処理期間の大幅短縮を図ることができるため処理コストを低減できる。
【図面の簡単な説明】
【図1】本発明の実施の形態における粘性質地盤浄化構築物を模式的に示す平面図である。
【図2】図1の粘性質地盤浄化構築物を模式的に示す断面図である。
【図3】本発明の実施の形態における粘性質地盤の浄化工法を説明する図である。
【符号の説明】
1 粘性土層
2 通気層
4 汚染層
5 通気柱
6 吸引孔
7 吸引ポイント
9 粘性質地盤
10 粘性質地盤浄化構築物
51 通気柱の通気層部分
61 吸引孔の通気層部分
X、Y ガス状の汚染物質の流れ方向
WL 地下水位
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a viscous ground purification structure and a purification method for purifying gaseous pollutants present in ground above the groundwater level in a viscous ground having a ventilation layer below the viscous soil layer.
[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.
[0003]
As a method for purifying such contaminated soil and contaminated groundwater, conventionally, a well is dug around the contaminated ground area and pumped to pump the pollutant dissolved in the pumped groundwater to an aeration treatment device or activated carbon on the ground. Groundwater pumping method that collects with an adsorption treatment device, or a soil gas suction method that sucks gaseous pollutants that exist in the ground above the groundwater level and that are lower than the groundwater level, and collects the contaminants with an activated carbon adsorption treatment device on the ground and so on.
[0004]
[Problems to be solved by the invention]
However, the application range and purification efficiency of the groundwater pumping method and soil gas suction method are greatly affected by the ground conditions. That is, the groundwater pumping method and the soil gas suction method are effective methods with good purification efficiency in sandy gravel ground or sandy ground with high water permeability or air permeability, but in viscous ground with low water permeability or air permeability, Since the range of influence of pumping water or gas suction is small and the purification efficiency is poor, the processing cost may be enormous or even difficult to apply. In particular, in ground with a high altitude such as a hill, the groundwater level is deep in the ground, and gaseous pollutants may be present above the groundwater level, and the ground is, for example, sandy ground. However, the groundwater pumping method is not applicable.
[0005]
Therefore, the object of the present invention is to apply the soil gas suction method to the viscous ground with low air permeability where the contaminated layer exists in the ground above the groundwater level, and the purification efficiency is high and the treatment period is greatly shortened. It is in providing the viscous ground purification structure and purification method which can aim at.
[0006]
[Means for Solving the Problems]
In such a situation, the present inventors have conducted intensive studies, and as a result, in a viscous ground having a ventilation layer below the viscous soil layer, the groundwater level is located below the ventilation layer or the ventilation layer and is lower than the groundwater level. A large number of ventilation pillars were created at an appropriate pitch on the ground where the contaminated layer exists above, and the air permeability of the ground was improved. Then, the gas suction device was operated and disposed in the ventilation layer portion of the suction hole. If a purification method that collects gaseous pollutants on the ground via the suction point is adopted, the soil gas suction method can be applied even to viscous ground with low air permeability. The present inventors have found that the processing cost can be reduced because it can be greatly shortened, and the present invention has been completed.
[0007]
That is, the present invention (1) is a viscous ground having a ventilation layer below the viscous soil layer, wherein the groundwater level is located below the ventilation layer or the ventilation layer, and the contaminated layer is above the groundwater level. A structure for purifying existing ground, the suction hole penetrating the viscous soil layer and reaching the ventilation layer; and a gas suction device for arranging a suction point in the ventilation layer portion of the suction hole; A viscous ground purification structure comprising a sand pile or a crushed stone pile distributed around the gas suction device and penetrating through the viscous soil layer to reach at least the ventilation layer is provided.
[0008]
Further, the present invention (2) is a viscous ground having a ventilation layer below the viscous soil layer, wherein the groundwater level is located below the ventilation layer or the ventilation layer, and the contaminated layer is above the groundwater level. A large number of sand piles or crushed stone piles were created on the existing ground at an appropriate pitch to improve the air permeability of the viscous soil layer, and then the gas suction device was operated and installed in the ventilation layer portion of the suction hole The present invention provides a viscous ground purification method for recovering the gaseous pollutant to the ground via a suction point.
[0009]
According to the present invention, it is possible to apply the soil gas suction method even in a viscous ground with low air permeability where a contaminated layer exists in the ground above the groundwater level, and the purification efficiency is improved, and the treatment period is greatly shortened. Therefore, the processing cost can be reduced.
[0010]
DETAILED DESCRIPTION OF THE INVENTION
Next, the purification method of the viscous ground in the embodiment of the present invention will be described with reference to FIGS. FIG. 1 is a plan view schematically showing the purification structure of the viscous ground of this example, FIG. 2 is a cross-sectional view schematically showing the purification structure of FIG. 1, and FIG. 3 explains the purification method of the viscous ground of this example Each figure is shown. In addition, the arrow in FIG. 3 shows the flow of a gaseous pollutant.
[0011]
The viscous ground purification structure 10 in the present embodiment is a viscous ground 9 having a ventilation layer 2 below the viscous soil layer 1, the groundwater level WL is located below the ventilation layer 2 or the ventilation layer 2, and the groundwater This is a structure for purifying the ground where the contaminated layer 4 exists above the position WL. In the present invention, the viscous ground 9 is not particularly limited as long as it has the ventilation layer 2 below the viscous soil layer 1, and the ratio of the viscous soil layer 1 and the ventilation layer 2 occupying in the viscous ground 9 is used. It is not limited. That is, the viscous ground 9 includes both a ground in which the thickness of the viscous soil layer 1 is equal to or greater than that of the ventilation layer 2 and a ground in which the thickness of the ventilation layer 2 is greater than the thickness of the viscous soil layer 1. .
[0012]
The viscous ground 9 is not particularly limited as long as it has the ventilation layer 2 below the viscous soil layer 1, and may have a surface layer portion above the viscous soil layer 1. The viscous soil layer 1 is a ground called silty or clay, and the ventilation layer 2 is a ground called a sandy soil layer or a gravel soil layer. Moreover, as a pollutant, the volatile organic chlorine compound etc. which exist in gaseous form are mentioned. The contaminated layer 4 contaminated with the pollutant is usually present in the viscous soil layer 1 above the natural groundwater level WL, but is not limited to this. For example, it exists from the viscous soil layer 1 to the ventilation layer 2. You may do it.
[0013]
The suction hole 6 penetrates the viscous soil layer 1 and further reaches the ventilation layer 2, and for example, a hollow tube or the like is used. The depth of the ventilation layer portion 61 of the suction hole 6 may be as long as the suction point 7 of the gas suction device can be installed, but may reach the groundwater level WL as shown in FIG. The gas suction device is not particularly limited as long as the suction point 7 is disposed in the ventilation layer portion 61 of the suction hole 6, and has a pump body near the suction point, or the pump body is located at the place. Instead, suction may be performed by a ground vacuum pump through a suction pipe connected to the suction point 7. Further, the place where the suction point 7 is disposed is not particularly limited, but it is the ventilation layer portion 61 of the suction hole 6 and the vicinity of the surface of the ventilation layer 2. This is preferable in that the substance can be sucked immediately and the diffusion of contaminants in the ventilation layer 2 can be prevented.
[0014]
The ventilation column 5 is intended to improve the air permeability of the viscous soil layer 1 and is not particularly limited as long as it is distributed around the suction point 7. It penetrates the cohesive soil layer 1 and reaches at least the ventilation layer 2. Therefore, the bottom of the vent column 5 is used up to the surface of the vent layer 2, the one in the middle of the vent layer 2, or the one that penetrates the vent layer 2 and reaches the groundwater level WL (see FIG. 2). it can. Among these, the thing with the lower end part of the ventilation column 5 to the surface of the ventilation layer 2 is suitable at the point that the construction material of the ventilation column 5 can be saved and a construction work period can also be shortened. As the ventilation column 5, a sand pile and a crushed stone pile can be used. The sand pile and the crushed stone pile can be constructed by a known sand pile construction method. Specifically, a sand drain construction method can be applied in which a sand pile is formed by discharging sand inserted into the pipe after the hollow pipe has been penetrated to the design depth in the ground and then pulled out to the ground surface. The viscous soil layer 1 in which the contaminated layer 4 exists has a ventilation path formed by the formation of the large number of ventilation columns 5, so that the air permeability is enhanced. For this reason, application of the soil gas suction method to the viscous soil layer 1 becomes practical, and the purification efficiency for the contaminated viscous ground, which has been difficult in the past, is increased. Moreover, the ground strength of the viscous soil layer 1 can be raised by creation of a sand pile or a crushed stone pile.
[0015]
The interval between the ventilation pillars 5 distributed around the suction point 7 is appropriately determined based on the ground conditions and the requirements of the purification period. That is, when the clay soil layer 1 is a silty ground, the spacing between the ventilation columns 5 can be increased. When the clay soil is a clay soil, the spacing between the ventilation columns 5 is decreased. Thus, according to the air permeability of a viscous soil layer, the placement interval of the ventilation column 5 is appropriately determined. Moreover, when the purification period can be extended, the interval between the ventilation columns 5 can be increased. When the purification period is desired to be shortened, the interval between the ventilation columns 5 is decreased. As described above, the placement interval of the ventilation columns 5 is appropriately determined even in accordance with the request for the purification period.
[0016]
In the viscous ground purification structure 10 of this example, a shielding wall (not shown) may be formed so as to surround the contaminated layer 4. The shielding wall divides the purification target area where the contaminated layer 4 is present and the other non-purification area, and can prevent the contaminant from flowing out to the non-purification area. The shielding wall is not particularly limited, and a pullable steel sheet pile can be used. For example, a shielding wall that penetrates the viscous soil layer 1 and the ventilation layer 2 where the contaminated layer 4 exists and reaches the groundwater level WL is suitable.
[0017]
A construction method for purifying the viscous ground using the purification structure 10 will be described with reference to FIG. First, the ground conditions and the contamination status are grasped, the size of the purification structure 10 is determined, and the above-described purification structure 10 is constructed. That is, in the viscous ground 9 having the ventilation layer 2 below the viscous soil layer 1 and the ground where the groundwater level WL is located in the ventilation layer 2 and the contaminated layer 4 exists above the groundwater level WL, the ventilation column 5 is formed at an appropriate pitch to improve the air permeability of the viscous soil layer 1 (FIG. 2). From this state, the gas suction device is operated.
[0018]
Gaseous contaminants present in the contamination layer 4 flow into the ventilation column 5 by the suction action of the suction point 7 (in the direction of arrow X in FIG. 3). Next, the air flow sucked in the contaminant moves downward in the ventilation column 5 and reaches the ventilation layer portion 51 of the ventilation column 5, and similarly, the suction point 7 sucks the inside of the ventilation layer 2 by the suction action of the suction point 7. Flows in the direction (in the direction of arrow Y in FIG. 3). Subsequently, it is recovered from the suction point 7 to the ground surface by a suction pipe (not shown). The contaminant contained in the suction gas is recovered by a known ground recovery device such as an activated carbon adsorption processing device. Such treatment of contaminants is performed until the concentration of contamination in the suction gas becomes a certain value or less.
[0019]
According to the purification method of the viscous ground 9 using such a purification structure 10, the viscous soil layer 1 in which the contaminated layer 4 is present is formed with an aeration path by the creation of the numerous ventilation columns 5. Air permeability is increased. For this reason, application of the soil gas suction method to the viscous soil layer 1 becomes practical, and the purification efficiency for the contaminated viscous ground, which has been difficult in the past, is increased.
[0020]
【The invention's effect】
According to the present invention, even if a contaminated layer exists in the ground above the groundwater level, and the ground is a viscous soil layer with low air permeability, the soil gas suction method can be applied, the purification efficiency is increased, and the treatment is performed. Since the period can be significantly shortened, the processing cost can be reduced.
[Brief description of the drawings]
FIG. 1 is a plan view schematically showing a viscous ground purification structure according to an embodiment of the present invention.
2 is a cross-sectional view schematically showing the viscous ground purification structure of FIG. 1. FIG.
FIG. 3 is a diagram for explaining a viscous ground purification method according to an embodiment of the present invention.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Cohesive soil layer 2 Ventilation layer 4 Contamination layer 5 Ventilation column 6 Suction hole 7 Suction point 9 Viscous ground 10 Viscous ground purification structure 51 Ventilation layer portion 61 of ventilation column Ventilation layer portion X, Y of suction hole Gaseous contamination Material flow direction WL Groundwater level

Claims (2)

粘性土層の下方に通気層を有する粘性質地盤で、地下水位が該通気層あるいは該通気層より下方に位置し且つ該地下水位よりも上方に汚染層が存在する地盤を浄化する構築物であって、該粘性土層を貫通し更に該通気層の中まで達する吸引孔と、吸引ポイントを該吸引孔の該通気層部分に配設するガス吸引装置と、該ガス吸引装置の周りに分散配設され、且つ該粘性土層を貫通し少なくとも該通気層まで達する砂杭又は砕石杭と、を備えることを特徴とする粘性質地盤浄化構築物。This is a structure that purifies the ground where the groundwater level is located below the aeration layer or above the aeration layer and the contamination layer exists above the groundwater level. A suction hole penetrating the viscous soil layer and reaching the ventilation layer, a gas suction device having a suction point disposed in the ventilation layer portion of the suction hole, and a distributed distribution around the gas suction device. And a sand pile or a crushed stone pile passing through the viscous soil layer and reaching at least the ventilation layer. 粘性土層の下方に通気層を有する粘性質地盤で、地下水位が該通気層あるいは該通気層より下方に位置し且つ該地下水位よりも上方に汚染層が存在する地盤に、砂杭又は砕石杭を適宜のピッチで多数造成して粘性土層の透気性の改善を図り、次いで、ガス吸引装置を稼動させ、吸引孔の通気層部分に配設された吸引ポイントを介して、該ガス状の汚染物質を地上に回収することを特徴とする粘性質地盤の浄化工法。A sand pile or crushed stone in a viscous ground having a ventilation layer below the viscous soil layer, in which the groundwater level is located below the ventilation layer or the ventilation layer, and the contaminated layer exists above the groundwater level. A large number of piles are formed at an appropriate pitch to improve the air permeability of the viscous soil layer, and then the gas suction device is operated and the gas state is passed through the suction point provided in the ventilation layer portion of the suction hole. A purification method for viscous ground, characterized by collecting the pollutants of the soil on the ground.
JP2001384127A 2001-12-18 2001-12-18 Viscous ground purification structure and purification method Expired - Fee Related JP3841339B2 (en)

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