JPH11169836A - Method for removing soil pollutant - Google Patents

Method for removing soil pollutant

Info

Publication number
JPH11169836A
JPH11169836A JP9363969A JP36396997A JPH11169836A JP H11169836 A JPH11169836 A JP H11169836A JP 9363969 A JP9363969 A JP 9363969A JP 36396997 A JP36396997 A JP 36396997A JP H11169836 A JPH11169836 A JP H11169836A
Authority
JP
Japan
Prior art keywords
water
horizontal well
culvert
horizontal
ground
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
JP9363969A
Other languages
Japanese (ja)
Inventor
Toshiaki Hirayama
利晶 平山
Masanobu Furukawa
正修 古川
Hitoshi Yamauchi
仁 山内
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.)
Kokusai Kogyo Co Ltd
Original Assignee
Kokusai Kogyo Co Ltd
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 Kokusai Kogyo Co Ltd filed Critical Kokusai Kogyo Co Ltd
Priority to JP9363969A priority Critical patent/JPH11169836A/en
Publication of JPH11169836A publication Critical patent/JPH11169836A/en
Pending legal-status Critical Current

Links

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for removing soil pollutants which surely prevents the pollution of the ground water by the soil pollutants by disposing plural horizontal wells constituting a water suction culvert at prescribed intervals and increasing the suction force of the gravity water in the unsaturation zones of the horizontal wells. SOLUTION: The culvert 1 is built by excavating the plural horizontal well holes apart the prescribed intervals W below the polluted zones 25 existing in the unsaturation zones 2. The gravity water 40 which dissolves the pollutants by penetrating in the ground through the polluted zones 25 from the ground surface GL is forcibly collected from the screen formed in the respective horizontal wells. Further, the collected gravity water 40 is discharged. The collection of the gravity water 40 into the horizontal wells 10a, 10b (10) is executed by sucking air into the horizontal wells 10 and drying the ground strata 31 on the peripheries of the horizontal well holes to induce capillarity in these parts.

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】本発明は土壌汚染物質の除去
方法に関し、更に詳細に言えば地下水面より上の地層で
ある不飽和帯に存在する硝酸性窒素、あるいはカドミウ
ム、砒素、銅、六化クロム、水銀のような重金属等の低
揮発性物質の除去方法であり、かかる土壌汚染物質を溶
解した雨水などが移動または降下浸透して帯水層に到達
する前に強制的に回収して、土壌汚染物質の浄化を可能
にした暗渠排水による土壌汚染物質の除去方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for removing soil contaminants, and more particularly to a method for removing nitrate nitrogen, cadmium, arsenic, copper, hexachloride existing in an unsaturated zone which is a layer above groundwater table. Chromium, a method of removing low-volatile substances such as heavy metals such as mercury, such as rainwater dissolved such soil contaminants move or descend and forcibly collect before reaching the aquifer, The present invention relates to a method for removing soil pollutants by culvert drainage that enables purification of soil pollutants.

【0002】[0002]

【従来の技術】通常、暗渠による排水には図6及び図7
に示すような構造の暗渠が用いられている。該暗渠1は
図7に示すように地表GLから地下水位WLとほぼ同一
の深さDに開削して、所定の間隔Wを隔てて複数の吸水
渠3を配設して地表GLから流下する重力水を吸水する
ようになっている。そして、前記複数の吸水渠3は吸水
渠3よりも深く掘削された集水渠4に接続していて、前
記吸水渠3から前記重力水を集水する。さらに、前記集
水渠4は水甲5を通じて集水渠4よりも一層深く掘削さ
れた排水路6に通じていて、前記集水路から前記重力水
を排水するようにしている。
2. Description of the Related Art Generally, drainage from a culvert is shown in FIGS.
A culvert having the structure shown in FIG. As shown in FIG. 7, the culvert 1 is cut from the ground surface GL to a depth D substantially equal to the groundwater level WL, and a plurality of water intake conduits 3 are arranged at predetermined intervals W to flow down from the ground surface GL. It is designed to absorb gravity water. The plurality of water inlets 3 are connected to a water drain 4 excavated deeper than the water inlet 3, and collect the gravity water from the water inlet 3. Further, the drainage channel 4 leads to a drainage channel 6 excavated deeper than the drainage channel 4 through the instep 5, so that the gravity water is drained from the drainage channel.

【0003】ところで、上記のような暗渠1の掘削は開
削により行われているため、暗渠を掘削するのは大規模
な工事を要するためコストアップとなり、しかも、長時
間を必要とした。そこで、近時、開削することなしに水
平井戸を掘削することによって、安価で短時間に暗渠を
掘削することが行われるようになってきた。
[0003] Since the culvert 1 is excavated as described above, digging the culvert requires a large-scale construction, which increases the cost and requires a long time. Therefore, recently, by excavating a horizontal well without digging, it has been practiced to excavate a culvert quickly and inexpensively.

【0004】すなわち、図2に示すような暗渠を構成す
る水平井戸10を掘削するには、図4に例示するように
所定の距離Lを隔てて両端に小ピットを穿設して一方を
貫入坑12とし、他方を到達坑13とする。地上に配置
されたパワーユニットトラック7を駆動してドリルユニ
ット14で案内しながらロッド8の先端のドリルヘッド
9に設けた掘削工具15を回転させ、貫入坑12から所
定の角度αで斜めに掘進する。その際、滑材として清水
などを掘削工具15の先端からジェット噴射させて土壌
を切り崩しながら水平井戸孔101を掘進する。なお、
ドリルヘッド9には発信器が設けられていて、この発信
器から発射される信号電波を地上においてフローケータ
16で検知してドリルヘッド9の掘進位置を確認する。
That is, in order to excavate a horizontal well 10 constituting a culvert as shown in FIG. 2, small pits are formed at both ends at a predetermined distance L as shown in FIG. The pit 12 and the other pit 13. The power unit truck 7 arranged on the ground is driven and the drilling tool 15 provided on the drill head 9 at the tip of the rod 8 is rotated while being guided by the drill unit 14, and the power unit truck 7 digs obliquely from the penetration pit 12 at a predetermined angle α. . At this time, fresh water or the like as a lubricating material is jetted from the tip of the drilling tool 15 to excavate the horizontal well hole 101 while cutting down the soil. In addition,
The drill head 9 is provided with a transmitter, and a signal wave emitted from the transmitter is detected on the ground by the flow locator 16 to confirm the drilling position of the drill head 9.

【0005】水平井戸10の掘進が終了したら、図5に
示すように前記ロッド8の先端には掘削工具15に代え
てリーマ17を取り付ける。さらに前記リーマ17に続
いて多数の孔18をあけてスクリーンSを構成した筒状
の井戸材料19をジョイント21を介して取り付けて、
滑材である清水などをジェット噴射させながら前記リー
マ17を回転させ、図5に矢印Bで示すように水平井戸
孔101の掘削方向とは反対方向に移動させることによ
り水平井戸孔101を拡径する。これと同時に、井戸材
料19を狭い水平井戸孔101に強制的に引き込むこと
によって水平井戸10を形成する。
When the excavation of the horizontal well 10 is completed, a reamer 17 is attached to the tip of the rod 8 in place of the excavation tool 15 as shown in FIG. Further, a cylindrical well material 19 having a large number of holes 18 formed in the screen S following the reamer 17 to form a screen S is attached via a joint 21.
The reamer 17 is rotated while jetting a lubricating material such as fresh water, and is moved in a direction opposite to the excavation direction of the horizontal well hole 101 as shown by an arrow B in FIG. I do. At the same time, the horizontal well 10 is formed by forcibly drawing the well material 19 into the narrow horizontal well hole 101.

【0006】[0006]

【発明が解決しようとする課題】ところで、前記の暗渠
を構成する水平井戸10の掘削方法によれば、安価にか
つ短時間に水平井戸を掘削することが可能になったが、
井戸材料19を狭い井戸孔内に強制的に引き込むから、
水平井戸孔101の壁面が圧縮されて透水性や通気性が
きわめて悪くなり、垂直井戸に比して単位スクリーン長
当たりの吸水量が少なくなるという問題があった。
According to the method for excavating the horizontal well 10 constituting the culvert described above, the horizontal well can be excavated inexpensively and in a short time.
Since the well material 19 is forcibly drawn into the narrow well hole,
There is a problem that the wall surface of the horizontal well hole 101 is compressed and the water permeability and air permeability become extremely poor, and the amount of water absorption per unit screen length becomes smaller than that of the vertical well.

【0007】そして、土壌汚染物質が硝酸塩や重金属等
の低揮発性物質である場合には、該土壌汚染物質は汚染
帯25(図1)に停滞しているが、一旦降雨や降雪があ
るとこの低揮発性汚染物質は雨水や雪解け水などに溶け
出して図7に示すように重力水40として徐々に帯水層
20へ向けて降下浸透する。従来の暗渠では前記重力水
の全てを捕捉することができず、その結果、帯水層20
への土壌汚染物質の浸入を招来し、土壌汚染や地下水汚
染の広がりを阻止するのは困難であった。
When the soil contaminants are low volatile substances such as nitrates and heavy metals, the soil contaminants stay in the contaminated zone 25 (FIG. 1). This low-volatility pollutant dissolves in rainwater, snowmelt, or the like, and gradually descends and permeates toward the aquifer 20 as gravity water 40 as shown in FIG. Conventional culverts cannot capture all of the gravitational water, resulting in aquifer 20
It has been difficult to prevent the spread of soil and groundwater pollution by causing soil contaminants to enter the area.

【0008】本発明の目的は、かかる従来の問題点を解
決するためになされたもので、暗渠を構成する複数の水
平井戸を所定の間隔に設け、かつ暗渠の重力水吸引力を
高めて土壌汚染物質による土壌の広範な汚染を確実に防
止するようにした土壌汚染物質の除去方法を提供するこ
とにある。
SUMMARY OF THE INVENTION An object of the present invention is to solve such a conventional problem. A plurality of horizontal wells constituting a culvert are provided at predetermined intervals, and the gravity water suction force of the culvert is increased to improve the soil. It is an object of the present invention to provide a method for removing soil pollutants, which surely prevents the soil from being extensively contaminated by pollutants.

【0009】[0009]

【課題を解決するための手段】本発明は土壌汚染物質の
除去方法であり、前述した技術的課題を解決するために
以下のように構成されている。すなわち、本発明の土壌
汚染物質の除去方法はは、不飽和帯に存在する汚染帯の
下方に所定の間隔をあけて複数の水平井戸孔を掘削して
暗渠を構築する工程と、地表から汚染帯に浸透して汚染
物質を溶解した重力水を前記各水平井戸に形成されたス
クリーンから強制的に集水する工程と、前記集水された
重力水を排出する工程とを含み、前記汚染物質の溶解し
た重力水が帯水層に到達するのを防止することを特徴と
する(請求項1)。
SUMMARY OF THE INVENTION The present invention is a method for removing soil pollutants, and is configured as follows to solve the above-mentioned technical problems. That is, the method for removing soil contaminants of the present invention comprises the steps of: constructing a culvert by digging a plurality of horizontal well holes at predetermined intervals below a contaminated zone existing in an unsaturated zone; Forcibly collecting gravitational water having permeated the zone to dissolve the contaminant from a screen formed in each of the horizontal wells, and discharging the collected gravitational water, the method comprising: The gravitational water in which the water is dissolved is prevented from reaching the aquifer (claim 1).

【0010】本発明において、前記暗渠1を構成する複
数の水平井戸孔101の間隔は前記汚染物質を溶解して
降下浸透する雨水などを確実に捕捉するに十分な距離で
あり、当該地層の透水性などの土質条件に応じて設定さ
れる。また、前記重力水は、降雪や降雨により地中に浸
透する天水、河川水や湖沼水である地表水を含むものと
する。
In the present invention, the interval between the plurality of horizontal well holes 101 constituting the culvert 1 is a distance sufficient to dissolve the pollutant and to reliably capture rainwater that descends and penetrates. It is set according to soil conditions such as the nature. The gravity water includes surface water, which is rainwater, river water, lake water, and the like, which penetrates into the ground due to snowfall or rainfall.

【0011】また、前記土壌汚染物質を溶解する重力水
を水平井戸に形成されたスクリーンから強制的に集水す
るには、ファンやブロア、コンプレッサなどにより井戸
孔内の空気を減圧して暗渠周辺の地層を乾燥させ、重力
水を強制的に集水するのが好ましい。
In order to forcibly collect gravitational water for dissolving the soil contaminants from a screen formed in a horizontal well, the air in the well hole is decompressed by a fan, a blower, a compressor, or the like to reduce the pressure around the culvert. It is preferable to dry the formation and forcefully collect gravity water.

【0012】さらに、集水された動力水を排出するに
は、地上設置型の自給式ポンプ(真空ポンプ)や水中ポ
ンプなどを使用することが好ましい。
Further, in order to discharge the collected power water, it is preferable to use a self-contained pump (vacuum pump) or a submersible pump which is installed on the ground.

【0013】また、土壌汚染物質の除去方法は、前述し
た必須の構成要素からなるが、その構成要素が具体的に
以下のような場合であっても成立する。すなわち、前記
水平井戸内に強制的に重力水を集水する工程は、水平井
戸の内部に空気を吸引して水平井戸孔の周辺の地層を乾
燥させて乾燥ゾーンを形成し、該乾燥ゾーンに生じる毛
管現象により前記重力水を井戸孔の内部に吸引すること
を特徴とする(請求項2)。
The method for removing soil contaminants comprises the above-mentioned essential components, but the above-described method is also applicable to the following cases. That is, in the step of forcibly collecting gravity water in the horizontal well, the air is sucked into the horizontal well to dry the stratum around the horizontal well hole to form a drying zone, and the drying zone is formed. The gravitational water is sucked into the well hole by a capillary action that occurs (claim 2).

【0014】本発明において、前記井戸孔の周囲の地層
を乾燥状態にするには、ファンやブロア、コンプレッサ
などで井戸内の空気を減圧して吸引して真空乾燥させた
り、あるいは水平井戸孔101内に風速を大にして空気
を送ったり、熱風を送るなど適宜の有効な手段を講ずる
ことができる。
In the present invention, in order to dry the formation around the well hole, the air in the well is decompressed and sucked by a fan, a blower, a compressor, or the like, and dried in a vacuum. Appropriate effective means such as sending air at a high wind speed or sending hot air can be taken.

【0015】本発明に係る土壌汚染物質の除去方法によ
れば、地表から浸透する過程の重力水は水平井戸孔に強
制的に集水される。そのため、地上から汚染帯を経て地
中に浸透する重力水に溶融した汚染物質は重力水と一緒
に水平井戸内に集められて排出されることになり、帯水
層に流下して地下水を汚染するようなことが防止され
る。
According to the method for removing soil pollutants according to the present invention, gravity water in the process of infiltrating from the ground surface is forcibly collected in the horizontal well hole. Therefore, the contaminants dissolved in the gravity water that permeates the ground through the pollution zone from the ground will be collected and discharged together with the gravity water in the horizontal well, flow down to the aquifer, and contaminate the groundwater. Is prevented.

【0016】[0016]

【発明の実施の形態】以下、本発明の土壌汚染物質の除
去方法を図に示される実施形態について更に詳細に説明
する。ただし、この実施の形態に記載されている構成部
品の寸法、材質、形状、その相対的配置などは特に特定
的な記載がない限りは、この発明の範囲をそれのみに限
定する趣旨ではなく、単なる説明例にすぎない。図1に
は本発明の一実施形態に係る土壌汚染物質の除去方法に
用いられる暗渠を含む地層の断面と、暗渠を構成する水
平井戸が降下浸透する重力水を吸引する時の状態を示
す。また、図2は図1のII−II線における暗渠を構成す
る水平井戸の断面、図3は井戸周辺の空気の吸引過程を
示す水平井戸の部分断面を示す。図4、図5は水平井戸
の掘削状態の説明図である。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the method for removing soil pollutants of the present invention will be described in more detail with reference to an embodiment shown in the drawings. However, the dimensions, materials, shapes, relative arrangements, and the like of the components described in this embodiment are not intended to limit the scope of the present invention thereto, unless otherwise specified. It is only an illustrative example. FIG. 1 shows a section of a stratum including a culvert used in a method for removing soil contaminants according to an embodiment of the present invention, and a state where a horizontal well constituting the culvert suctions gravitational water that descends and penetrates. FIG. 2 is a cross-sectional view of a horizontal well constituting the culvert along the line II-II in FIG. 1, and FIG. 3 is a partial cross-sectional view of the horizontal well showing an air suction process around the well. 4 and 5 are explanatory diagrams of a state of excavating a horizontal well.

【0017】図1において地表GLの下方の不飽和帯2
には硝酸性窒素や重金属などの低揮発性の土壌汚染物質
が土壌に含まれている汚染帯25が存在する。この汚染
帯25の下方に所定の深さDaと間隔Wをもち、図4及
び図5に示すように掘削された複数の水平井戸10a、
10bを掘削して暗渠1を構築する。前記水平井戸10
a、10bは地上に開口する一対の開口部23、24を
有するとともに、水平井戸孔101に井戸材料19を挿
通する。
In FIG. 1, the unsaturated zone 2 below the ground surface GL
There is a contaminated zone 25 in which soil contains low volatile soil contaminants such as nitrate nitrogen and heavy metals. A plurality of horizontal wells 10a having a predetermined depth Da and an interval W below the contaminated zone 25 and excavated as shown in FIGS.
The culvert 1 is constructed by excavating 10b. The horizontal well 10
a and 10b have a pair of openings 23 and 24 opening to the ground, and the well material 19 is inserted into the horizontal well hole 101.

【0018】なお、図1においては2本の水平井戸10
a、10bのみを示してあるが、汚染帯25の広さや土
質に応じて3本以上の水平井戸を、適宜掘削することが
できることは言うまでもない。さらに、暗渠1の下方に
は不透水層29の上方に帯水層20が位置する。
In FIG. 1, two horizontal wells 10 are provided.
Although only a and 10b are shown, it goes without saying that three or more horizontal wells can be excavated as appropriate according to the size and soil quality of the contaminated zone 25. Furthermore, the aquifer 20 is located below the culvert 1 and above the impermeable layer 29.

【0019】前記一方の開口部23には地上にブロア
(図示せず)が配置されている。該ブロアの吐出側から
水平井戸孔101に圧縮空気を高速で送り込むようにし
てある。また、前記他方の開口部24側には、地上設置
型の自給式ポンプ(図示せず)が設置され、水平井戸内
に集水された動力水を排出するようになっている。
A blower (not shown) is disposed on the ground in the one opening 23. Compressed air is sent from the discharge side of the blower into the horizontal well hole 101 at a high speed. A ground-based self-contained pump (not shown) is provided on the other opening 24 side to discharge the motive water collected in the horizontal well.

【0020】ブロアを駆動して、図3に示すように開口
部24側から水平井戸孔101の内部に空気を高速で流
すことにより井戸内部の空気は減圧され、井戸周辺の地
層の空気Aを水平井戸10のスクリーンSの多数の孔1
8から吸引する。この空気の流れによって水平井戸10
の周辺の地層は真空乾燥される。このため、乾燥された
地層は土粒子同士の間には微小なスキマが生じた状態と
なる。
The air inside the well is depressurized by driving the blower to flow air from the opening 24 side into the horizontal well hole 101 at a high speed as shown in FIG. Many holes 1 in screen S of horizontal well 10
Aspirate from 8. The horizontal well 10
The stratum around is vacuum dried. For this reason, the dried stratum is in a state in which minute gaps are generated between the soil particles.

【0021】図1に示すように、上記の水平井戸10の
周辺の地層は等水圧線35aで囲まれ、かつ水平井戸1
0a、10bを直接囲む乾燥ゾーン31となる。さら
に、前記乾燥ゾーン31の周囲には等水圧線35bに囲
まれた半乾燥ゾーン32が形成される。そして、前記半
乾燥ゾーン32の周囲を囲む等水圧線35cに囲まれる
湿潤ゾーン33が形成される。等水圧線35は水平井戸
10(10a、10b)の中心に向けて水圧は次第に低
くなっていく。
As shown in FIG. 1, the stratum around the horizontal well 10 is surrounded by iso-pressure lines 35a, and
The drying zone 31 directly surrounds 0a and 10b. Further, a semi-dry zone 32 is formed around the drying zone 31 and is surrounded by the iso-pressure line 35b. Then, a wet zone 33 is formed which is surrounded by the iso-pressure line 35c surrounding the semi-dry zone 32. The water pressure of the iso-pressure line 35 gradually decreases toward the center of the horizontal well 10 (10a, 10b).

【0022】かくして、降雨や降雪により地表GLから
地中に浸透した重力水40は、図1に示すように不飽和
帯2内を重力により自然流下する。乾燥ゾーン31では
前述したように図示しない土粒子相互の間には微小なス
キマを生じているので、毛管現象が生じて水分量の相違
によって重力水40は水平井戸10a、10bのスクリ
ーンSを構成する多数の孔18から水平井戸孔101内
に強制的に吸引される。なお、隣接する水平井戸とは所
定の間隔Wに設定してあり、水平井戸に吸引されないで
帯水層20に浸透するような重力水41aの移動または
降下浸透が生じることはない。
Thus, the gravitational water 40 that has infiltrated into the ground from the ground surface GL due to rainfall or snowfall naturally flows down in the unsaturated zone 2 by gravity as shown in FIG. In the drying zone 31, as described above, minute gaps are generated between the soil particles (not shown), so that a capillary phenomenon occurs, and the gravitational water 40 forms the screen S of the horizontal wells 10a and 10b due to a difference in water content. From the large number of holes 18 into the horizontal well hole 101. Note that a predetermined interval W is set between the horizontal well and the adjacent horizontal well, so that the gravity water 41a does not move or descend and permeate so as to permeate the aquifer 20 without being sucked into the horizontal well.

【0023】次いで、図示しない地上設置型の自給式ポ
ンプや水中ポンプを作動させて重力水40を排出する。
その後、動力水に溶解している硝酸性窒素や重金属を動
力水から分離処理して土壌の浄化を行う。
Next, a gravitational water 40 is discharged by operating a self-contained pump or a submersible pump (not shown) installed on the ground.
Thereafter, nitrate nitrogen and heavy metals dissolved in the motive water are separated from the motive water to purify the soil.

【0024】さらに、図1の右側に位置する水平井戸1
0bのように下部にトレイ36を設置すると、水平井戸
10の上方から降下する重力水40を受けて下流に流す
ことによって水平井戸10で吸収できなかった重力水4
0がさらに降下して帯水帯20に浸透して土壌を広く汚
染するようなことは防止される。
Further, a horizontal well 1 located on the right side of FIG.
If the tray 36 is installed at the lower part as shown in FIG. 0b, the gravity water 40 which falls from above the horizontal well 10 and flows downstream, and the gravity water 4 which cannot be absorbed by the horizontal well 10
It is prevented that 0 further descends and penetrates into the aquifer 20 to widely pollute the soil.

【0025】[0025]

【発明の効果】以上説明したように、本発明の土壌汚染
物質の除去方法によれば、不飽和帯に存在する汚染帯の
下方に所定の間隔をあけて水平井戸を配置し、地表から
汚染帯を経て地中に浸透して汚染物質を溶解する重力水
を水平井戸に形成されたスクリーンから強制的に集水す
るので、前記水平井戸に前記重力水を確実に捕捉するこ
とができ、帯水層への前記重力水が移動するのを防止す
ることによって、土壌汚染を効果的に阻止することが可
能になる。
As described above, according to the method for removing soil contaminants of the present invention, horizontal wells are arranged at predetermined intervals below the contaminated zone existing in the unsaturated zone, and contaminated soil is removed from the ground surface. Since gravitational water that permeates into the ground and dissolves contaminants through the band is forcibly collected from the screen formed in the horizontal well, the gravitational water can be reliably captured in the horizontal well. By preventing the gravity water from migrating to the water layer, soil pollution can be effectively prevented.

【0026】しかも、前記井戸内の空気を移動させて井
戸周辺の地層を乾燥させることにより、毛管現象により
重力水を強制的に井戸孔内に吸引するので、帯水層への
前記の汚染物質を溶解した重力水の移動がより確実に防
止される。
Further, by moving the air in the well and drying the stratum around the well, the gravity water is forcibly sucked into the well hole by capillary action. The movement of gravity water in which water is dissolved is more reliably prevented.

【0027】さらに、水平井戸の下部にトレイを設置す
ると、前記重力水を井戸内に捕捉することができない事
態が生じても、前記トレイが前記汚染物質を溶解する重
力水を受けて、これを排出することができるから、汚染
物質の帯水層への浸透による汚染の広がりをなお一層確
実に阻止することができる。
Further, if a tray is provided below the horizontal well, even if the gravitational water cannot be captured in the well, the tray receives the gravitational water for dissolving the contaminants and removes it. Since the water can be discharged, the spread of the contamination due to the infiltration of the pollutant into the aquifer can be more reliably prevented.

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

【図1】本発明の一実施形態に係る土壌汚染物質の除去
方法に用いられる暗渠を含む地層の断面図である。
FIG. 1 is a cross-sectional view of a stratum including a culvert used in a method for removing soil contaminants according to an embodiment of the present invention.

【図2】図1のII−II線における断面図であって、暗渠
を構成する水平井戸を示す。
FIG. 2 is a cross-sectional view taken along the line II-II of FIG. 1, showing a horizontal well forming a culvert.

【図3】井戸周辺の空気の吸引過程を示す水平井戸の部
分断面図である。
FIG. 3 is a partial cross-sectional view of a horizontal well showing a process of sucking air around the well.

【図4】水平井戸の掘進状態を示す概略図である。FIG. 4 is a schematic view showing a state of excavation of a horizontal well.

【図5】水平井戸への井戸材料の組み込み状態を示す概
略図である。
FIG. 5 is a schematic view showing a state where well materials are incorporated into a horizontal well.

【図6】従来の暗渠暗渠の開削状態を示す平面図であ
る。
FIG. 6 is a plan view showing an open state of a conventional culvert.

【図7】図6のVII−VII線における断面図である。FIG. 7 is a sectional view taken along line VII-VII in FIG. 6;

【符号の説明】[Explanation of symbols]

1 暗渠 2 不飽和帯 10 水平井戸 101 水平井戸孔 20 帯水層 25 汚染帯 31 乾燥ゾーン 36 トレイ 40 重力水 GL 地表 S スクリーン W 水平井戸の間隔 Reference Signs List 1 culvert 2 unsaturated zone 10 horizontal well 101 horizontal well hole 20 aquifer 25 polluted zone 31 drying zone 36 tray 40 gravity water GL ground surface S screen W horizontal well interval

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 不飽和帯に存在する汚染帯の下方に所定
の間隔をあけて複数の水平井戸孔を掘削して暗渠を構築
する工程と、地表から汚染帯に浸透して汚染物質が溶解
した重力水を前記各水平井戸に形成されたスクリーンか
ら強制的に集水する工程と、前記集水された重力水を排
出する工程とを含み、前記汚染物質の溶解した重力水が
帯水層に移動するのを防止することを特徴とする土壌汚
染物質の除去方法。
1. A step of digging a plurality of horizontal well holes at predetermined intervals below a contaminated zone existing in an unsaturated zone to construct a culvert, and dissolving contaminants by permeating the contaminated zone from the ground surface. Forcibly collecting the collected gravitational water from the screen formed in each of the horizontal wells, and discharging the collected gravitational water, wherein the gravitational water in which the contaminants are dissolved is aquifer. A method for removing soil contaminants, wherein the method comprises preventing migration to soil.
【請求項2】 前記水平井戸内に強制的に重力水を集水
する工程は、水平井戸の内部に空気を吸引して水平井戸
孔の周辺の地層を乾燥させて乾燥ゾーンを形成し、該乾
燥ゾーンに生じる毛管現象により前記重力水を井戸孔の
内部に吸引することを特徴とする土壌汚染物質の除去方
法。
2. The step of forcibly collecting gravity water in the horizontal well, wherein air is sucked into the horizontal well to dry a stratum around the horizontal well hole to form a drying zone. A method for removing soil contaminants, wherein the gravity water is sucked into a well hole by capillary action occurring in a drying zone.
JP9363969A 1997-12-17 1997-12-17 Method for removing soil pollutant Pending JPH11169836A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9363969A JPH11169836A (en) 1997-12-17 1997-12-17 Method for removing soil pollutant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9363969A JPH11169836A (en) 1997-12-17 1997-12-17 Method for removing soil pollutant

Publications (1)

Publication Number Publication Date
JPH11169836A true JPH11169836A (en) 1999-06-29

Family

ID=18480652

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9363969A Pending JPH11169836A (en) 1997-12-17 1997-12-17 Method for removing soil pollutant

Country Status (1)

Country Link
JP (1) JPH11169836A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003033757A (en) * 2001-07-26 2003-02-04 Kajima Corp Contaminated soil spread-preventing method
CN110228860A (en) * 2019-07-15 2019-09-13 大连地拓环境科技有限公司 One kind being used for Abandoned Land of Mine pollution prevention system
CN113753981A (en) * 2021-09-17 2021-12-07 河北省地矿局第三水文工程地质大队 Fourth series underground water and soil pollution treatment method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003033757A (en) * 2001-07-26 2003-02-04 Kajima Corp Contaminated soil spread-preventing method
CN110228860A (en) * 2019-07-15 2019-09-13 大连地拓环境科技有限公司 One kind being used for Abandoned Land of Mine pollution prevention system
CN113753981A (en) * 2021-09-17 2021-12-07 河北省地矿局第三水文工程地质大队 Fourth series underground water and soil pollution treatment method

Similar Documents

Publication Publication Date Title
US6207114B1 (en) Reactive material placement technique for groundwater treatment
RU2067138C1 (en) Plant for prevention of seepage of contaminated water from waste storage and method for construction of device for trapping seeped water from waste storage
KR101841511B1 (en) Vacuum well drainage system for underground water level lowering
JP3508997B2 (en) How to clean contaminated soil
JP3497116B2 (en) Spring water filtration method and apparatus
JPH11169836A (en) Method for removing soil pollutant
JP2006326397A (en) System and method for purification of contaminated ground
Gabr et al. BTEX extraction from clay soil using prefabricated vertical drains
KR100719444B1 (en) Level of underground water lowering method and deep well point system thereof
JP4376760B2 (en) Groundwater absorption device and groundwater absorption method
JP2000027170A (en) Groundwater level lowering device, ground improvement method and strainer device
CN115710039A (en) Circulating well repairing system and method
JP2002346539A (en) Method for cleaning polluted soil
BRPI0417843B1 (en) process to remove contaminants from contaminated soil
JP4480169B2 (en) Soil purification method
JP2001214451A (en) Ground-water level lowering method and its equipment
CN111807492B (en) NAPL pollution restoration system in underground water based on pollution control and restoration method thereof
JP2011021349A (en) Rainwater permeation pit excavator, construction method for laying rainwater permeation pipe, and rainwater permeation structure
JPH05208181A (en) Facility for gas removal from waste buried reclaimed ground
JP3738028B1 (en) Floating oil purification device and contaminated formation purification method using the same
JP2002001296A (en) Method for decontaminating contaminated ground and strengthening ground at the same time
JP2007083196A (en) Method and apparatus for eliminating soil contaminant
JP7296902B2 (en) Oil recovery system and oil recovery method
JP3934580B2 (en) Contaminated ground purification method using both in-situ agitation and air injection suction, and purification device used therefor
JP2894539B2 (en) Aquifer pollution investigation device and its investigation method