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JP2002370084A - How to reclaim contaminated soil - Google Patents

How to reclaim contaminated soil

Info

Publication number
JP2002370084A
JP2002370084A JP2001180540A JP2001180540A JP2002370084A JP 2002370084 A JP2002370084 A JP 2002370084A JP 2001180540 A JP2001180540 A JP 2001180540A JP 2001180540 A JP2001180540 A JP 2001180540A JP 2002370084 A JP2002370084 A JP 2002370084A
Authority
JP
Japan
Prior art keywords
water
contaminated soil
water collecting
contaminated
pipe
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2001180540A
Other languages
Japanese (ja)
Inventor
Yoji Oku
要治 奥
Akira Sawaguchi
明 澤口
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Airec Engineering Corp
Original Assignee
Airec Engineering Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Airec Engineering Corp filed Critical Airec Engineering Corp
Priority to JP2001180540A priority Critical patent/JP2002370084A/en
Publication of JP2002370084A publication Critical patent/JP2002370084A/en
Pending legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Water Treatment By Sorption (AREA)
  • Investigation Of Foundation Soil And Reinforcement Of Foundation Soil By Compacting Or Drainage (AREA)

Abstract

(57)【要約】 【課題】 産業廃棄物を殆ど産出することなく、処理作
業に多くの手間や費用を要しない汚染土壌の再生方法を
提供する。 【解決手段】 汚染土壌S地域の境界近傍にシートパイ
ル1を打ち込んで区画し、その内側に集水槽2を兼ねた
発進立坑と到達立坑を掘削形成し、発進立坑から到達立
坑に向けて水平方向よりやや上向きに案内管を圧入し、
案内管が到達立坑に達したら、案内管の先端部に集水管
3の一端を連結して引き込むことにより集水管3を汚染
土壌S中に埋設し、汚染土壌S中の汚染物質Pを雨水等
に溶出させ、この汚染水を集水管3を通って集水槽2中
に集積させ、汚染水中に含まれる汚染物質Pを凝集剤F
等に吸着させた後、凝集剤F等を回収して廃棄するよう
にした。
(57) [Summary] [PROBLEMS] To provide a method for reclaiming contaminated soil that hardly generates industrial waste and does not require much labor and cost for treatment. SOLUTION: A sheet pile 1 is driven into the vicinity of a boundary of a contaminated soil S area to be partitioned, and a starting shaft and a reaching shaft which also serve as a water collecting tank 2 are excavated and formed inside the pile, and a horizontal direction from the starting shaft to the reaching shaft is formed. Press the guide tube slightly upwards,
When the guide pipe reaches the reaching shaft, one end of the water collection pipe 3 is connected to the leading end of the guide pipe and pulled in, so that the water collection pipe 3 is buried in the contaminated soil S, and the contaminant P in the contaminated soil S is removed by rainwater or the like. The contaminated water is accumulated in the water collecting tank 2 through the water collecting pipe 3 and the contaminant P contained in the contaminated water is coagulant F
Then, the coagulant F and the like are collected and discarded.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は重金属、油類等で汚
染された土壌から汚染物質を回収することにより土壌を
再生させる汚染土壌の再生方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method of reclaiming contaminated soil by reclaiming soil by recovering contaminants from soil contaminated with heavy metals, oils and the like.

【0002】[0002]

【従来の技術】半導体製造工場やメッキ工場、石油製品
工場の跡地等では土壌が有害重金属や油類で汚染されて
いる場合がある。これらの有害物質は雨水等と共に地中
に滲み込んで、地下水や他の場所に溶出する等の二次災
害が発生するといった、いわゆる環境問題の重要な課題
の一つになっている。
2. Description of the Related Art In some cases, such as a former site of a semiconductor manufacturing plant, a plating plant, and a petroleum product plant, soil is contaminated with harmful heavy metals and oils. These harmful substances infiltrate into the ground together with rainwater and the like, and have become one of the important so-called environmental problems such as secondary disasters such as dissolution into groundwater and other places.

【0003】このような汚染土壌対策としては、汚染土
壌を掘削して取り除き、汚染されない土壌で埋め戻した
り、原因物質が重金属である場合は、汚染土壌を直接セ
メントで固化することにより雨水や地下水への溶出を防
止したり、原因物質が油類である場合は汚染土壌を焼却
炉で焼却して油類を揮発させたりしていた。
[0003] As a countermeasure against such contaminated soil, the contaminated soil is excavated and removed, and the contaminated soil is backfilled with non-contaminated soil. If the causative substance is a heavy metal, the contaminated soil is directly solidified with cement to remove rainwater or groundwater. If the causative substance is oil, the contaminated soil was incinerated in an incinerator to evaporate the oil.

【0004】しかし、何れの方法によっても莫大な処理
費用と作業時間を要するばかりでなく、多量の産業廃棄
物が生成されたり、汚染対策が不十分になる等のため、
あまり現実的な処理対策とはなっていなかった。そこ
で、例えば、特開平10-102471号公報には、汚染土壌に
対して50〜100重量%の生石灰と、これに5〜10重量%
の珪酸ナトリウムを添加混合した後、約40重量%の水を
注入して生石灰の水和反応を喚起させ、重金属は珪酸塩
として、油類は反応時に生成する珪酸カルシウムゲルに
吸着させて水に対して不溶性の物質に変性させるように
した土壌の汚染処理方法の発明が開示されている。
[0004] However, not only do both methods require enormous disposal costs and operation time, but also a large amount of industrial waste is generated and pollution control becomes insufficient.
It was not a very realistic treatment measure. Thus, for example, Japanese Patent Application Laid-Open No. 10-102471 discloses that 50 to 100% by weight of quicklime and 5 to 10% by weight of
After adding and mixing the sodium silicate, water of about 40% by weight is injected to induce a hydration reaction of quick lime, heavy metals are converted into silicates, and oils are adsorbed on calcium silicate gel generated during the reaction to form water. There is disclosed an invention of a method for treating soil contamination which is modified into an insoluble substance.

【0005】[0005]

【発明が解決しようとする課題】上述の土壌の汚染処理
方法により、汚染処理に要する費用や作業時間はある程
度軽減できるものの、重金属と結合させるため等に使用
される薬剤を大量に消費しなければならないため、多額
の処理費用を要すると共に、薬剤を反応させて重金属等
と結合させなければならないため、汚染土壌を掘り起こ
すか、無数の注入孔を掘削して薬剤を注入するかしなけ
ればならず、手間の掛かる処理作業となっており、しか
も土壌中には汚染物質が残存しているといった問題点も
あった。
Although the cost and work time required for the pollution treatment can be reduced to some extent by the above-mentioned method for treating the soil, the chemical used for binding with heavy metals must be consumed in a large amount. Because of this, a large amount of processing cost is required, and the chemicals must be reacted and combined with heavy metals, etc., so that contaminated soil must be excavated, or a myriad of injection holes must be excavated to inject the chemicals. This is a troublesome processing operation, and there is a problem that contaminants remain in the soil.

【0006】本発明は従来技術におけるかかる問題点を
解消すべく為されたものであり、産業廃棄物を殆ど産出
することなく、処理作業に多くの手間や費用を要しない
汚染土壌の再生方法を提供することを目的とする。
The present invention has been made to solve such a problem in the prior art, and a method for regenerating contaminated soil which does not produce much industrial waste and does not require much labor and cost for the disposal work. The purpose is to provide.

【0007】[0007]

【課題を解決するための手段】上記課題を解決するため
に本発明は、汚染土壌地域に汚染水を貯留するための集
水槽を掘削形成すると共に、周囲に多数の導水孔が穿設
された多数の集水管を、一端が集水槽中に開口し、略水
平で集水槽に向かってやや傾斜するように、汚染土壌中
に圧入埋設し、雨水等に汚染物質が溶出した汚染水が集
水管を通って集水槽中に貯留し、該集水槽中に投入され
た凝集剤あるいは吸着剤に汚染水中に溶出した汚染物質
を吸着させ、該凝集剤等を回収するようにしたものであ
り、好ましくは、汚染土壌地域に掘削形成した集水槽に
対向する位置に到達立坑を掘削し、集水槽内から案内管
を略水平で集水槽に向かってやや傾斜するように、汚染
土壌中に圧入し、到達立坑側に到達した案内管の先端部
に集水管の一端を連結させた後、案内管を介して集水管
を汚染土壌中に引き込んで埋設したものである。
According to the present invention, a water collecting tank for storing contaminated water in a contaminated soil area is formed by excavation, and a plurality of water introduction holes are formed around the water collecting tank. A large number of water collection pipes are buried under pressure in contaminated soil so that one end opens into the water collection tank and is approximately horizontal and slightly inclined toward the water collection tank. Is stored in a water collecting tank through which the contaminant eluted in the contaminated water is adsorbed by the coagulant or the adsorbent put into the water collecting tank, and the coagulant or the like is recovered, preferably Excavates a shaft to reach a position opposite to the water collection tank formed in the contaminated soil area, and presses the guide tube from the inside of the water collection tank into the contaminated soil so that it is almost horizontal and slightly inclined toward the water collection tank, At the tip of the guide tube that has reached the arrival shaft side, After sintering, through the guide tube in which is embedded draws water collecting pipe in the contaminated soil.

【0008】[0008]

【発明の実施の形態】以下図面を参照して本発明の実施
例を詳細に説明する。図1は本発明の実施例に係る汚染
土壌の再生を実施するための集水設備を示す地中断面模
式図、図2は同じく、汚染土壌の再生処理が進行した状
態を示す集水設備の地中断面模式図である。これらの図
において、1は汚染土壌S地域を区画して汚染物質Pの
他の地域への拡散を防止するために、境界部に所定深さ
まで埋設された鋼板等で成るシートパイル、2は汚染土
壌S中の汚染物質Pを回収するために、汚染土壌S地域
の境界近くに地表から掘削形成された、後述する発進立
坑を兼ねた集水槽、3は汚染土壌S中に集水槽2に向か
って若干の傾斜を有して多数、圧入埋設された集水管、
31は汚染土壌S中から滲み出した雨水等の浸水を集水
管3中に導入するために、それらの下面を除く全面に亘
って多数穿設された導水孔である。
Embodiments of the present invention will be described below in detail with reference to the drawings. FIG. 1 is a schematic diagram of an underground section showing a water collecting facility for regenerating contaminated soil according to an embodiment of the present invention, and FIG. It is an underground cross section schematic diagram. In these figures, reference numeral 1 denotes a sheet pile made of a steel plate or the like buried to a predetermined depth at a boundary portion in order to partition the contaminated soil S area to prevent the diffusion of the contaminant P to other areas, and 2 denotes a contaminated soil. In order to collect the contaminants P in the soil S, a water collecting tank formed also from the surface near the boundary of the contaminated soil S area and serving as a starting shaft, which will be described later, 3 faces the water collecting tank 2 in the contaminated soil S. A large number of water pipes buried under pressure with a slight slope,
Reference numeral 31 denotes a plurality of water guide holes formed over the entire surface except for the lower surface thereof for introducing inundation such as rainwater oozing out of the contaminated soil S into the water collecting pipe 3.

【0009】図5は集水管3の斜視図である。集水管3
は市販の鋼管、ビニール管等で形成され、導水孔31は
集水管3の下側には穿設しないことにより、雨水等がそ
の下面側から流出するのを防止している。導水孔31の
径はその穿設密度や汚染土壌Sの土質によって多少異な
るが、土砂の流入を防止しながら、効率良く浸水を導入
し得るようにするために、3〜12mmφの範囲で選定する
のが良い。また、集水管3の材質は耐腐食性、価格優位
性の観点からビニール管が好適である。
FIG. 5 is a perspective view of the water collecting pipe 3. Water collecting pipe 3
Is formed of a commercially available steel pipe, vinyl pipe, or the like, and the water guide hole 31 is not formed below the water collecting pipe 3 to prevent rainwater or the like from flowing out from the lower surface side. The diameter of the water introduction hole 31 is slightly different depending on the drilling density and the soil quality of the contaminated soil S, but is selected in a range of 3 to 12 mmφ in order to prevent the inflow of the earth and sand and to efficiently introduce the inundation. Is good. The material of the water collecting pipe 3 is preferably a vinyl pipe from the viewpoint of corrosion resistance and price advantage.

【0010】次に、本実施例に係る集水設備の構築方法
を説明する。図3および図4は集水設備の構築方法を説
明するための地中断面模式図であり、図3はその第一工
程、図4はその第二工程を示している。これらの図にお
いて、4は集水槽2となる発進立坑から掘削する到達目
標となる到達立坑、5は発進立坑底面に設置される下押
装置、6は次に述べる案内管を導いて汚染土壌S中を突
き進む先端装置、7は集水管3を導くための案内(パイ
ロット)管、8は案内管7と集水管3とを接続する連結
筒である。
Next, a method of constructing a water collecting facility according to the present embodiment will be described. FIG. 3 and FIG. 4 are schematic cross-sectional views of the underground for explaining the method of constructing the water collecting facility. FIG. 3 shows the first step and FIG. 4 shows the second step. In these figures, 4 is a reaching shaft which is a target to be excavated from the starting shaft which becomes the water collecting tank 2, 5 is a push-down device installed on the bottom surface of the starting shaft, and 6 is a contaminated soil S by guiding a guide tube described below. A tip device for pushing the inside, 7 is a guide (pilot) pipe for guiding the water collecting pipe 3, and 8 is a connecting cylinder connecting the guide pipe 7 and the water collecting pipe 3.

【0011】まず、汚染土壌S地域の境界近傍を囲むよ
うにシートパイル1を打ち込んで汚染地域を区画すると
共に、その内側両端に集水槽2を兼ねた発進立坑と到達
立坑4を掘削する。そして、発進立坑底面に下押装置5
を設置する。次に、下押装置5に案内管7を取り付け、
その先端に先端装置6を螺着した後、下押装置5を駆動
させて案内管7を介して先端装置6を汚染土壌S中に押
し込む。そして、先端装置6の進入に連れて、案内管7
を順次連結する(図3参照)。先端装置6には、その頭
部を油圧で揺動させる揺動機構と、磁界を発生する電磁
コイルが設けられ、案内管7を介してそれぞれ油圧ケー
ブルおよび電線ケーブルで下押装置5に接続されてい
る。この電磁コイルから発した磁界は地表に移動自在に
設置された磁界検知装置により検知され、先端装置6の
所在位置が検出されるようになっている。
First, a sheet pile 1 is driven so as to surround the vicinity of the boundary of the contaminated soil S area to partition the contaminated area, and a start shaft and a reaching shaft 4 which also serve as the water collecting tanks 2 are excavated at both inner ends thereof. Then, a push-down device 5 is provided on the bottom of the starting shaft.
Is installed. Next, the guide tube 7 is attached to the lower push device 5,
After the tip device 6 is screwed to the tip, the pushing device 5 is driven to push the tip device 6 into the contaminated soil S via the guide tube 7. Then, as the tip device 6 enters, the guide tube 7
Are sequentially connected (see FIG. 3). The tip device 6 is provided with a rocking mechanism for rocking its head by hydraulic pressure and an electromagnetic coil for generating a magnetic field, and is connected to the push-down device 5 via a guide tube 7 by a hydraulic cable and an electric wire cable, respectively. ing. The magnetic field generated from the electromagnetic coil is detected by a magnetic field detection device movably installed on the ground surface, and the position of the tip device 6 is detected.

【0012】こうして得られた先端装置6の所在位置情
報に基づいて先端装置6が適正な方向に進行しているか
否かが判定され、適正な方向でなかった場合は、向き修
正指令が下押装置5に発せられ、その下押装置5の図示
しない向き修正油圧機構が駆動されて、先端装置6の頭
部の向きが揺動機構により修正される。先端装置6の進
行方向は到達立坑4に向かって若干上昇するように設定
される。
Based on the location information of the tip device 6 obtained in this way, it is determined whether or not the tip device 6 is proceeding in an appropriate direction. It is emitted to the device 5, and the direction correcting hydraulic mechanism (not shown) of the lowering device 5 is driven, and the direction of the head of the tip device 6 is corrected by the swinging mechanism. The traveling direction of the tip device 6 is set so as to slightly rise toward the reaching shaft 4.

【0013】先端装置6が到達立坑4に到達すると、案
内管7から先端装置6を取り外し、その跡に連結筒8を
取り付け、この連結筒8の後端に集水管3の一端を取り
付ける。そして、下押装置5を逆駆動して案内管7群を
引き込み、これに連れて連結筒8を介して集水管3を案
内管7が通った貫通孔に沿って引き込む。この引き込み
時は案内管7の押し込み時と丁度逆に、貫通孔から引き
出された案内管7を順次取り外していく。最後に連結筒
8が貫通孔から引き出されたら、連結筒8を集水管3の
一端から取り外して当該集水管3の引き込み作業を終了
する。こうして、汚染土壌S中を万遍なく、所定間隔を
おいて多段に多数の集水管3を非開先で埋設する。全て
の集水管3の埋設が終了したら、到達立坑4を埋め戻し
て集水設備の構築作業を終了する。
When the tip device 6 reaches the reaching shaft 4, the tip device 6 is removed from the guide tube 7, and a connecting tube 8 is attached to the trail, and one end of the water collecting tube 3 is attached to the rear end of the connecting tube 8. Then, the lower pushing device 5 is driven in reverse to draw in the guide pipes 7, and along with this, the water collecting pipes 3 are drawn in along the through holes through which the guide pipes 7 pass. At the time of this retraction, the guide tube 7 pulled out from the through hole is sequentially removed just opposite to the time when the guide tube 7 is pushed. Finally, when the connecting tube 8 is pulled out from the through-hole, the connecting tube 8 is removed from one end of the water collecting pipe 3 and the drawing operation of the water collecting pipe 3 is completed. In this way, a large number of water collecting pipes 3 are buried in the contaminated soil S at predetermined intervals at equal intervals without any gap. When all the water collecting pipes 3 have been buried, the reaching shaft 4 is backfilled to complete the construction of the water collecting facility.

【0014】集水設備が構築された後、汚染土壌S中の
汚染物質Pが雨水や地下水に溶け出し、汚染水が最寄り
の導水孔31から集水管3内に流れ込む。流入した汚染
水は集水槽2に向かって若干傾斜して埋設された集水管
3に沿って集水槽2側に流下し、集水槽2中に貯留す
る。なお、降水量が少ない場合や汚染物質Pの回収を急
ぎたい場合は、汚染土壌Sの地表に人為的に散水すると
良い。また、汚染物質Pが水に溶け易い重金属の場合
は、雨水や地下水を介して回収できるが、油類の場合は
容易に水に溶けないので、地表に界面活性剤を散布した
り、界面活性剤を溶かした水を散水する。
After the water collecting facility is constructed, the contaminants P in the contaminated soil S dissolve into rainwater and groundwater, and the contaminated water flows into the water collecting pipe 3 from the nearest water inlet 31. The inflowing contaminated water flows down to the water collecting tank 2 along the buried collecting pipe 3 slightly inclined toward the water collecting tank 2 and is stored in the water collecting tank 2. When the amount of precipitation is small or when it is desired to quickly collect the pollutant P, water may be artificially sprayed on the surface of the contaminated soil S. When the contaminant P is a heavy metal that is easily soluble in water, it can be recovered through rainwater or groundwater. However, in the case of oils, the contaminant P is not easily dissolved in water. Sprinkle water with the agent dissolved.

【0015】図1に示すように、集水槽2中には予め、
製紙汚泥等の材料を焼却して作られた人工ゼオライト
(組成は例えば、SO2 62.7% CaCO3 15.5% Al2O3 7.2% K
2O 2.8% Fe2O3 0.3% TiO2 0.2% Na2O 0.2%)等の凝集剤
Fあるいは多孔質の吸着剤が投入されていて、汚染水が
集水槽2中に流れ込むと、汚染物質Pは図6に示すよう
に、凝集剤Fの微細孔中に取り込まれ、吸着される。凝
集剤Fの吸着作用は凝集剤Fの局部と汚染物質Pが逆極
性のイオンになっているため、静電吸引力が働いて生じ
ると考えられている。凝集剤Fに汚染物質Pが十分吸着
されたと考えられる所定期間が経過したら、集水槽2底
部に沈殿した凝集剤Fを吸引ポンプで水と共に汲み上げ
回収する。回収した凝集剤F等は乾燥させた後、産業廃
棄物として廃棄される。
As shown in FIG. 1, the water collecting tank 2
Material incineration to made artificial zeolites such as papermaking sludge (composition for example, SO 2 62.7% CaCO 3 15.5 % Al 2 O 3 7.2% K
If a flocculant F or a porous adsorbent such as 2 O 2.8% Fe 2 O 3 0.3% TiO 2 0.2% Na 2 O 0.2%) is charged and the contaminated water flows into the collection tank 2, the contaminant P is taken into the fine pores of the flocculant F and adsorbed, as shown in FIG. It is considered that the adsorption action of the coagulant F is caused by the electrostatic attraction force because the local part of the coagulant F and the contaminant P are ions of opposite polarities. After a lapse of a predetermined period in which it is considered that the contaminant P has been sufficiently adsorbed to the flocculant F, the flocculant F settled at the bottom of the water collecting tank 2 is pumped and collected together with water by a suction pump. The collected flocculant F and the like are dried and then discarded as industrial waste.

【0016】このように、本実施例では汚染土壌S中の
汚染物質Pを雨水等に溶出させ、この汚染物質Pを含む
汚染水を汚染土壌S中に埋設した集水管3を通って集水
槽2中に集積させ、汚染水中に含まれる汚染物質Pを凝
集剤F等に吸着させた後、凝集剤F等を回収して廃棄す
るようにしたので、汚染物質Pを除去するために多量の
薬剤を消費する必要がなく、汚染物質Pを除去するため
の集水設備の主要な構成は汚染土壌S中に圧入埋設した
多数の集水管3と、これらの集水管3が連通する集水槽
2だけなので、集水設備を構築するのに大掛かりな機械
設備を必要としないから、汚染土壌S中の汚染物質Pを
除去して再生させるのに要する手間と費用を大幅に低減
できる。なお、本実施例では汚染物質Pを凝集剤F等に
吸着させるようにしたが、多量の降水や多量の水の給水
源を確保できるようであれば、凝集剤F等を用いずに、
集水槽2中に貯留した汚染水を吸引ポンプで汲み上げて
浄化した後、排水するようにしても良い。
As described above, in the present embodiment, the contaminant P in the contaminated soil S is eluted into rainwater or the like, and the contaminated water containing the contaminant P is passed through the water collecting pipe 3 embedded in the contaminated soil S to collect water. After the contaminant P contained in the contaminated water is adsorbed on the coagulant F or the like, the coagulant F or the like is collected and discarded. The main structure of the water collecting equipment for removing the pollutants P without consuming the chemical is a large number of water collecting pipes 3 buried under pressure in the contaminated soil S and a water collecting tank 2 to which these water collecting pipes 3 communicate. Since no large-scale mechanical equipment is required to construct the water collecting facility, the labor and cost required for removing and regenerating the pollutant P in the contaminated soil S can be greatly reduced. In this embodiment, the contaminant P is adsorbed on the coagulant F or the like. However, if it is possible to secure a large amount of precipitation and a large amount of water supply source, the coagulant F is not used.
The contaminated water stored in the water collecting tank 2 may be drained after being purified by being pumped up by a suction pump.

【0017】[0017]

【発明の効果】以上説明したように請求項1記載の発明
によれば、汚染土壌地域に集水槽を掘削形成すると共
に、周囲に多数の導水孔が穿設された多数の集水管を、
一端が集水槽中に開口し、略水平で集水槽に向かってや
や傾斜するように、汚染土壌中に圧入埋設し、汚染水が
集水管を通って集水槽中に貯留し、そこに投入された凝
集剤あるいは吸着剤に汚染物質を吸着させて、それを回
収するようにしたので、産業廃棄物を殆ど産出せず、処
理作業に要する手間や費用を大幅に省くことができる。
As described above, according to the first aspect of the present invention, a water collecting tank is excavated and formed in a contaminated soil area, and a number of water collecting pipes having a number of water introducing holes formed therearound are provided.
One end opens into the collection tank, and is buried in the contaminated soil so as to be substantially horizontal and slightly inclined toward the collection tank, and the contaminated water is stored in the collection tank through the collection pipe and injected into it. Since the contaminant is adsorbed on the flocculant or the adsorbent and the collected contaminant is recovered, almost no industrial waste is produced, and the labor and cost required for the processing operation can be greatly reduced.

【0018】請求項2記載の発明によれば、汚染土壌地
域に掘削形成した集水槽に対向する位置に到達立坑を掘
削し、集水槽内から案内管を略水平で集水槽に向かって
やや傾斜するように、汚染土壌中に圧入し、到達立坑側
に到達した案内管の先端部に集水管の一端を連結させた
後、案内管を介して集水管を汚染土壌中に引き込んで埋
設したので、汚染土壌中に集水管を効率良く圧入させ埋
設することができる。
According to the second aspect of the present invention, the reaching shaft is excavated at a position facing the water collecting tank formed in the contaminated soil area, and the guide pipe is inclined substantially horizontally from the water collecting tank toward the water collecting tank. After that, one end of the water collection pipe was connected to the tip of the guide pipe that reached the reaching shaft side by injecting it into the contaminated soil, and then the water collection pipe was drawn into the contaminated soil through the guide pipe and buried. In addition, a water collection pipe can be efficiently pressed into and buried in contaminated soil.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の実施例に係る汚染土壌の再生を実施す
るための集水設備を示す地中断面模式図
FIG. 1 is a schematic diagram of an underground cross section showing a water collecting facility for regenerating contaminated soil according to an embodiment of the present invention.

【図2】同じく、汚染土壌の再生処理が進行した状態を
示す集水設備の地中断面模式図
FIG. 2 is a schematic diagram of an underground cross-section of a water collecting facility showing a state in which a process of regenerating contaminated soil has progressed.

【図3】集水設備の構築方法の第一工程を説明するため
の地中断面模式図
FIG. 3 is a schematic diagram of an underground cross section for explaining a first step of a method of constructing a water collecting facility.

【図4】集水設備の構築方法の第二工程を説明するため
の地中断面模式図
FIG. 4 is an underground cross-sectional schematic view for explaining a second step of the method of constructing the water collecting facility.

【図5】集水管の斜視図FIG. 5 is a perspective view of a water collecting pipe.

【図6】凝集剤に汚染物質が吸着される状況を示す説明
FIG. 6 is an explanatory view showing a situation in which a contaminant is adsorbed on a flocculant.

【符号の説明】[Explanation of symbols]

1 シートパイル 2 集水槽 3 集水管 4 到達立坑 5 下押装置 6 先端装置 7 案内管 8 連結筒 31 導水孔 F 凝集剤 P 汚染物質 S 汚染土壌 REFERENCE SIGNS LIST 1 sheet pile 2 water collecting tank 3 water collecting pipe 4 reaching shaft 5 lowering device 6 tip device 7 guide tube 8 connecting tube 31 water guide hole F coagulant P pollutant S contaminated soil

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 2D043 DA04 DD15 4D004 AA41 AB02 AB03 AC07 4D015 BA19 BB05 CA06 CA17 DA35 DC04 EA32 FA03 FA30 4D024 AA04 AB04 AB16 BA07 DA10 DB01 DB21  ──────────────────────────────────────────────────続 き Continued on front page F term (reference) 2D043 DA04 DD15 4D004 AA41 AB02 AB03 AC07 4D015 BA19 BB05 CA06 CA17 DA35 DC04 EA32 FA03 FA30 4D024 AA04 AB04 AB16 BA07 DA10 DB01 DB21

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 重金属、油類等で汚染された土壌から汚
染物質を回収することにより土壌を再生させる汚染土壌
の再生方法において、汚染土壌地域に汚染水を貯留する
ための集水槽を掘削形成すると共に、周囲に多数の導水
孔が穿設された多数の集水管を、一端が前記集水槽中に
開口し、略水平で前記集水槽に向かってやや傾斜するよ
うに、汚染土壌中に圧入埋設し、雨水等に汚染物質が溶
出した汚染水が前記集水管を通って前記集水槽中に貯留
し、該集水槽中に投入された凝集剤あるいは吸着剤に汚
染水中に溶出した汚染物質を吸着させ、該凝集剤あるい
は吸着剤を回収するようにしたことを特徴とする汚染土
壌の再生方法。
1. A method for reclaiming contaminated soil by reclaiming soil by collecting contaminants from soil contaminated with heavy metals, oils, etc., wherein a water collecting tank for storing contaminated water in a contaminated soil area is formed. At the same time, a large number of water collection pipes having a large number of water introduction holes formed around them are pressed into the contaminated soil so that one end of the water collection pipe is opened in the water collection tank and is substantially horizontal and slightly inclined toward the water collection tank. Contaminated water buried and eluted with contaminants in rainwater etc. is stored in the water collecting tank through the water collecting pipe, and the contaminants eluted in the contaminated water into the flocculant or the adsorbent charged in the water collecting tank A method for reclaiming contaminated soil, wherein the method comprises adsorbing and collecting the flocculant or the adsorbent.
【請求項2】 汚染土壌地域に掘削形成した集水槽に対
向する位置に到達立坑を掘削し、前記集水槽内から案内
管を略水平で前記集水槽に向かってやや傾斜するよう
に、汚染土壌中に圧入し、前記到達立坑側に到達した前
記案内管の先端部に集水管の一端を連結させた後、前記
案内管を介して前記集水管を汚染土壌中に引き込んで埋
設したことを特徴とする請求項1記載の汚染土壌の再生
方法。
2. A contaminated soil is excavated at a position facing a water collecting tank formed in the contaminated soil area, and a guide pipe is substantially horizontally inclined from the inside of the water collecting tank toward the water collecting tank. After connecting one end of the water collecting pipe to the tip of the guide pipe reaching the reaching shaft side, the water collecting pipe was drawn into the contaminated soil via the guide pipe and buried therein. The method for reclaiming contaminated soil according to claim 1.
JP2001180540A 2001-06-14 2001-06-14 How to reclaim contaminated soil Pending JP2002370084A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001180540A JP2002370084A (en) 2001-06-14 2001-06-14 How to reclaim contaminated soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001180540A JP2002370084A (en) 2001-06-14 2001-06-14 How to reclaim contaminated soil

Publications (1)

Publication Number Publication Date
JP2002370084A true JP2002370084A (en) 2002-12-24

Family

ID=19020945

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001180540A Pending JP2002370084A (en) 2001-06-14 2001-06-14 How to reclaim contaminated soil

Country Status (1)

Country Link
JP (1) JP2002370084A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005349349A (en) * 2004-06-14 2005-12-22 Kankyo Soken Kk Material for disposing of heavy metal
JP2006305543A (en) * 2005-03-29 2006-11-09 Kurita Water Ind Ltd In-situ containment method
JP2007032223A (en) * 2005-07-29 2007-02-08 Fudo Tetra Corp Contaminated groundwater removal equipment
JP2010029843A (en) * 2008-06-23 2010-02-12 Nittetsu Kankyo Engineering Kk Contaminated soil cleaning apparatus and contaminated soil cleaning method
KR100977151B1 (en) * 2008-03-06 2010-08-20 주식회사 대용이엔씨 Field cleaning method of contaminated soil using pipe propulsion
KR101451385B1 (en) 2014-04-18 2014-10-22 한국과학기술연구원 Method of monitoring purification state and investigating in-situ state of pollution for soil and groundwater
CN108043868A (en) * 2017-12-08 2018-05-18 常州大学 Soil with serious petroleum pollution repairs bed
CN111360054A (en) * 2020-03-26 2020-07-03 汪小琴 Hierarchical soil pollution administers device

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005349349A (en) * 2004-06-14 2005-12-22 Kankyo Soken Kk Material for disposing of heavy metal
JP2006305543A (en) * 2005-03-29 2006-11-09 Kurita Water Ind Ltd In-situ containment method
JP2007032223A (en) * 2005-07-29 2007-02-08 Fudo Tetra Corp Contaminated groundwater removal equipment
KR100977151B1 (en) * 2008-03-06 2010-08-20 주식회사 대용이엔씨 Field cleaning method of contaminated soil using pipe propulsion
JP2010029843A (en) * 2008-06-23 2010-02-12 Nittetsu Kankyo Engineering Kk Contaminated soil cleaning apparatus and contaminated soil cleaning method
KR101451385B1 (en) 2014-04-18 2014-10-22 한국과학기술연구원 Method of monitoring purification state and investigating in-situ state of pollution for soil and groundwater
CN108043868A (en) * 2017-12-08 2018-05-18 常州大学 Soil with serious petroleum pollution repairs bed
CN111360054A (en) * 2020-03-26 2020-07-03 汪小琴 Hierarchical soil pollution administers device

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