JP2006289300A - Purification method and apparatus of soil - Google Patents

Purification method and apparatus of soil Download PDF

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JP2006289300A
JP2006289300A JP2005115786A JP2005115786A JP2006289300A JP 2006289300 A JP2006289300 A JP 2006289300A JP 2005115786 A JP2005115786 A JP 2005115786A JP 2005115786 A JP2005115786 A JP 2005115786A JP 2006289300 A JP2006289300 A JP 2006289300A
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groundwater
soil
water
pumping
ground
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Inventor
Joji Murakami
譲二 村上
Toshihiro Takaine
敏浩 高稲
Osamu Endo
修 遠藤
Takashi Yanagisawa
隆 柳沢
Hiroshi Ishihara
廣士 石原
Tadaaki Nomura
忠明 野村
Hidenori Kodera
秀則 小寺
Shinichi Ikehata
伸一 池畑
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Kinjo Rubber Co Ltd
Tokyu Construction Co Ltd
Asanuma Corp
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Kinjo Rubber Co Ltd
Tokyu Construction Co Ltd
Asanuma Corp
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Priority to JP2005115786A priority Critical patent/JP2006289300A/en
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a purification method and an apparatus of soil easily and surely purifying soil by repeatedly washing soil without disturbing the ground in the whole region of soil containing pollutants. <P>SOLUTION: Soil containing pollutants is purified by repeatedly conducting: pumping up of polluted groundwater W1 by a pumping means 10; purification of the pumped-up polluted groundwater W1 by a purification plant 20; magnetic field treatment of purified water W2 obtained by purifying the polluted groundwater W1 by a magnetic treatment machine 30; supply of the magnetic field-treated water W3 obtained by magnetic field-treatment of purified water W2 to the ground G via a water passage 40; and raising of a groundwater level lowered by pumping up of the polluted groundwater W1 to a given level by temporarily stopping pumping up of water. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、汚染物質を含有する土壌を浄化する土壌の浄化方法および浄化装置に関する。   The present invention relates to a soil purification method and a purification device for purifying soil containing contaminants.

例えば硝酸性窒素は、農業活動において重要な肥料として使用されているが、多量に摂取すると中毒症状を引き起こす有害物質(汚染物質)であることが知られている。
ところが、肥料として繰り返し投入されることや生活廃棄物(生活排水を含む)や畜産廃棄物等に含まれていることなどにより土壌に蓄積された硝酸性窒素は、地下水に溶出することで、広域に汚染する場合があるとともに、汚染物質を含有した地下水が井戸等に流入することで人的な被害を引き起こす場合がある。
For example, nitrate nitrogen is used as an important fertilizer in agricultural activities, but is known to be a harmful substance (pollutant) that causes poisoning symptoms when consumed in large quantities.
However, nitrate nitrogen accumulated in soil due to repeated inputs as fertilizers, and contained in domestic waste (including domestic wastewater) and livestock waste, etc., is eluted into groundwater, resulting in a wide area. In some cases, groundwater containing pollutants flows into wells, etc., causing human damage.

同様に工場や廃棄物処分場等から流出して土壌に浸透した油分や揮発性有機化合物等も汚染物質として被害をもたらすことが知られている。
このように、多数の分野により引き起こされる土壌汚染が問題となっている。
Similarly, oils and volatile organic compounds that have flowed out of factories, waste disposal sites, etc., and have permeated the soil are also known to cause damage as pollutants.
Thus, soil contamination caused by many fields is a problem.

このような汚染物質を含有する土壌の浄化方法として、例えば、(1)原位置にて浄化材を汚染土壌に添加し、撹拌混合する方法(例えば、特許文献1参照)、(2)汚染土壌を掘削して洗浄した後、埋め戻す方法(例えば、特許文献2参照)、(3)汚染地下水を地中または地上において浄化した後、この浄化水を地中に注水することで地下水を循環させて汚染土壌を洗浄する方法(例えば、特許文献3参照)等、さまざまな技術が開発されており、実用化にいたっている。
特開2004−313997号公報([0009]−[0012]、図1−図3) 特開2005−040764号公報([0014]−[0019]、図1) 特開2003−181436号公報([0012]−[0016]、図2)
As a purification method of soil containing such contaminants, for example, (1) a method of adding a purification material to the contaminated soil in-situ and mixing with stirring (see, for example, Patent Document 1), (2) contaminated soil After excavating and washing the groundwater, refilling the groundwater (for example, see Patent Document 2), (3) After purifying the contaminated groundwater in the ground or on the ground, the groundwater is circulated by pouring the purified water into the ground Various techniques, such as a method for cleaning contaminated soil (see, for example, Patent Document 3) have been developed and put to practical use.
JP 2004-313997 A ([0009]-[0012], FIGS. 1 to 3) Japanese Patent Laying-Open No. 2005-040764 ([0014]-[0019], FIG. 1) Japanese Unexamined Patent Publication No. 2003-181436 ([0012]-[0016], FIG. 2)

ところが、原位置において浄化材を添加し撹拌混合する方法は、撹拌混合により地盤を乱し、地盤の強度を低下させるため、跡地の利用に弊害をもたらす場合があるという問題点を有していた。
また、汚染領域が広域にわたる場合、全汚染領域に対する撹拌混合作業に手間がかかり、時間と費用が嵩むという問題点も有していた。
However, the method of adding and purifying the purification material in-situ has the problem that the ground may be disturbed by stirring and mixing, and the strength of the ground may be reduced, which may cause adverse effects on the use of the site. .
In addition, when the contaminated area covers a wide area, there is a problem that it takes time and work to stir and mix the entire contaminated area, increasing time and cost.

また、掘削した土壌を洗浄する方法は、土量が多量な場合、作業に手間がかかるという問題点を有しているとともに、一旦掘削した土壌を埋め戻すことから、地盤の強度が低下し、跡地の利用に弊害をもたらす場合があるという問題点を有していた。   In addition, the method of cleaning the excavated soil has a problem that it takes time to work when the amount of soil is large, and since the excavated soil is backfilled, the strength of the ground decreases, There was a problem in that the use of the ruins might be harmful.

さらに、汚染地下水を浄化した後、地中に注水する、いわゆる揚水処理法では、循環される地下水が、同一の水みちを通ってしまい、地下水が浸透しにくいという問題がある。その結果、汚染物質が溶出されず、土壌の洗浄が不完全となる部分が発生する場合や、完全に土壌を洗浄するために多大な時間を要する場合があるなどの問題点を有していた。   Furthermore, in the so-called pumping treatment method, in which contaminated groundwater is purified and then poured into the ground, there is a problem that the groundwater that is circulated passes through the same water channel and the groundwater is difficult to permeate. As a result, there was a problem that the pollutant was not eluted and there was a part where washing of the soil was incomplete, or it took a lot of time to wash the soil completely. .

本発明は、このような問題点を解決するためになされたものであり、汚染物質を含有する土壌の領域全体について、地盤を乱すことなく繰り返し土壌の洗浄を行うことで簡易、かつ、確実に浄化を行うことを可能とした土壌の浄化方法および浄化装置を提案することを課題とする。   The present invention has been made to solve such problems, and it is simple and reliable by repeatedly washing the soil without disturbing the ground for the entire soil region containing the pollutant. It is an object of the present invention to propose a soil purification method and a purification device that enable purification.

前記課題を解決するために、請求項1に記載の発明は、地下水を利用して汚染物質を含有する土壌を洗浄する土壌の浄化方法であって、汚染領域の地下水を揚水して地下水の水位を低下させた後、前記地下水の揚水により低下した地下水の水位を上昇させることを繰り返し行うことを特徴としている。   In order to solve the above-mentioned problem, the invention described in claim 1 is a soil purification method for washing soil containing pollutants using groundwater, wherein the groundwater level is raised by pumping groundwater in a contaminated area. After lowering, the groundwater level lowered by pumping the groundwater is repeatedly raised.

かかる土壌の浄化方法によれば、地下水の揚水により地下水の水位(以下、単に「地下水位」という場合がある)を低下させることと、例えば揚水の量を調整する等により地下水の水位を上昇させることとを繰り返し行うことで、水位を上昇させるたびに地下水がまんべんなく汚染領域全体にいきわたり、汚染物質を含有する土壌を含む領域(以下、本明細書において「汚染領域」と称する場合がある)にある汚染物質を地下水に溶出させて回収するため、確実に土壌の浄化を行うことが可能となる。
また、この土壌の浄化方法によれば、揚水により地下水位を調整するのみで、確実に汚染物質を含有する土壌を洗浄することが可能であるため、施工性に優れている。さらに、地盤を乱すこともないため、跡地の利用の際に特別な処理工法(地盤改良工等)を要することがなく、全体として、経済性に優れている。
According to the soil purification method, the groundwater level is raised by lowering the level of groundwater (hereinafter sometimes simply referred to as “groundwater level”) and the level of the groundwater is increased by adjusting the amount of pumped water, for example. By repeating the above, every time the water level is raised, the groundwater is distributed evenly over the entire contaminated area, or in the area containing the soil containing the pollutant (hereinafter sometimes referred to as “contaminated area” in this specification). Since a certain pollutant is eluted and recovered in the groundwater, it is possible to reliably clean the soil.
Moreover, according to this soil purification method, it is possible to clean the soil containing the pollutant with certainty only by adjusting the groundwater level by pumping water, so that the workability is excellent. Further, since the ground is not disturbed, a special treatment method (ground improvement work or the like) is not required when using the former site, and the whole is excellent in economic efficiency.

また、前記土壌の浄化方法において、例えば注水井を利用するなどして、汚染領域に水分を供給すれば、揚水により地下水の水量が減少することがなく、周辺地域の地下水の流域を変化させることがないため、地盤沈下や井戸枯れなどの弊害が生じることがなく、現況の自然体系を維持することができ、好適である。
また、水分を汚染領域の地盤に積極的に供給することにより、地下水位の上昇の速度を調整することで、揚水時に土壌の間隙を流れる地下水の水みちを変化させることが可能となり、故に、土壌の洗浄を確実、かつ、早期に行うことが可能となる。
Further, in the soil purification method, if water is supplied to the contaminated area by using, for example, a water injection well, the amount of groundwater is not reduced by pumping, and the groundwater basin in the surrounding area is changed. Therefore, there is no adverse effect such as land subsidence or well withering, and the current natural system can be maintained, which is preferable.
In addition, by actively supplying moisture to the ground of the contaminated area, it becomes possible to change the water path of the groundwater flowing through the soil gap during pumping by adjusting the rate of rise of the groundwater level. Soil cleaning can be performed reliably and early.

また、前記土壌の浄化方法において汚染領域への水分の供給が、地表面から浸透させることにより行われれば、地下水位よりも上位の領域にある汚染物質もこの水分に溶出させて洗い流すことができるため、汚染領域の土壌の洗浄を確実に行うことが可能となる。   Moreover, if the supply of moisture to the contaminated area is performed by infiltrating from the ground surface in the soil purification method, the contaminants in the area above the groundwater level can also be eluted and washed away by this moisture. Therefore, it is possible to reliably clean the soil in the contaminated area.

また、前記土壌の浄化方法において汚染領域に浸透させる水分が、揚水された地下水を浄化した浄化水であれば、新たに水道水や海水等を採取する必要がなく、あるいは採取する量を削減することができるため、その設備や採取に要する費用を削減することができ、好適である。   In addition, if the water permeated into the contaminated area in the soil purification method is purified water obtained by purifying the pumped ground water, it is not necessary to newly collect tap water or seawater or reduce the amount to be collected. Therefore, it is possible to reduce the cost required for the equipment and collection, which is preferable.

さらに、前記土壌の浄化方法において、地中に浸透させる水分に、表面張力低下処理を施してあれば、地中への地下水の浸透を早めること、および、深く浸透させることが可能となり、好適である。   Furthermore, in the soil purification method, if surface tension reduction treatment is applied to the moisture that penetrates into the ground, it is possible to accelerate the penetration of groundwater into the ground and to penetrate deeply, which is preferable. is there.

また、請求項6に記載の発明は、地下水を利用して汚染物質を含有する土壌を洗浄する土壌の浄化方法であって、汚染領域の地下水を揚水するとともに、地表面から前記汚染領域に水分を浸透させることを特徴としている。   The invention according to claim 6 is a soil purification method for washing soil containing pollutants using groundwater, wherein the groundwater in the contaminated area is pumped up, and water from the ground surface is introduced into the contaminated area. It is characterized by making it penetrate.

かかる土壌の浄化方法によれば、地下水を、汚染物質を含有する領域内において地下水を積極的に流動させることにより、この地下水に汚染物質を溶出させて回収するため、土壌の洗浄を確実に行うことが可能となり、好適である。また、汚染領域への水分の供給は、地表面から浸透させることにより行うため、地下水位よりも上位の領域にある汚染物質に関しても、この水分に溶出させて洗い流すことができ、好適である。   According to the soil purification method, the groundwater is positively flowed in the area containing the pollutant, so that the groundwater is eluted and recovered, so that the soil is reliably washed. It is possible and preferable. In addition, since the supply of moisture to the contaminated area is performed by infiltrating from the ground surface, the contaminants in the area higher than the groundwater level can be eluted by this moisture and washed away.

また、前記土壌の浄化方法における水分が、前記揚水された地下水を浄化した浄化水であれば、地下水を循環させることで、地下水の流域を維持し、周辺地域の生態系等に影響を及ぼすことがないため、好適である。   In addition, if the water in the soil purification method is purified water obtained by purifying the pumped groundwater, circulating the groundwater maintains the groundwater basin and affects the surrounding ecosystem. This is preferable.

さらに、前記水分が、表面張力低下処理が施された後、地中に浸透されれば、浸透性に優れており、土壌の洗浄速度を早めるとともに汚染領域全体に地下水を浸透させて汚染物質を回収するため、早期、かつ、確実に土壌の浄化を行うことが可能となり、好適である。   Furthermore, if the moisture is infiltrated into the ground after being subjected to surface tension reduction treatment, the water is excellent in permeability, and the soil cleaning speed is increased and the groundwater is infiltrated into the entire contaminated area to remove contaminants. Since it collects, it becomes possible to clean up the soil early and reliably, which is preferable.

また、請求項9に記載の発明は、汚染物質を含有する土壌の浄化装置であって、汚染物質を含有する土壌を含む領域に配置された揚水手段と、前記揚水手段により揚水された地下水を浄化する浄化手段と、前記水分に表面張力低下処理を施す表面張力低下手段と、前記表面張力低下手段により表面張力低下処理が施された水分を地盤に供給する水分供給手段とを備えることを特徴としている。   The invention according to claim 9 is a device for purifying soil containing a pollutant, wherein pumping means disposed in an area including the soil containing pollutant, and groundwater pumped by the pumping means Purifying means for purifying, surface tension reducing means for subjecting the moisture to a surface tension reducing process, and moisture supplying means for supplying the ground subjected to the surface tension reducing process by the surface tension reducing means to the ground. It is said.

かかる土壌の浄化装置は、水分供給手段により供給された水分により土壌を洗浄するため、地盤を乱すことなく土壌が含有する汚染物質を回収し、浄化することを可能としており、好適である。   Such a soil purification apparatus is suitable because the soil is washed with the moisture supplied by the moisture supply means, and thus it is possible to collect and purify the contaminant contained in the soil without disturbing the ground.

さらに、前記土壌の浄化装置において、水分供給手段が、地表面に形成された水路や、地表面に前記水分を散布する散布手段であれば、広域に水分を供給することが可能となり、好適である。また、上方(地表面)から水分を浸透させることで、地下水位よりも上方における汚染物質を含有した土壌に関しても洗浄することを可能としており、好適である。   Further, in the soil purification apparatus, if the water supply means is a water channel formed on the ground surface or a spray means for spraying the water on the ground surface, it is possible to supply water over a wide area, which is preferable. is there. Moreover, by allowing water to permeate from above (the ground surface), it is possible to wash soil containing contaminants above the groundwater level, which is preferable.

本発明の土壌の浄化方法および浄化装置によれば、汚染物質を含有する土壌の領域全体について、地盤を乱すことなく繰り返し土壌の洗浄を行うことで簡易、かつ、確実に浄化を行うことが可能となる   According to the soil purification method and the purification apparatus of the present invention, it is possible to easily and reliably purify the entire soil region containing the pollutant by repeatedly washing the soil without disturbing the ground. Become

本発明の好適な実施の形態について、図面を参照して説明する。なお、説明において、同一要素には同一の符号を用い、重複する説明は省略する。
ここで、図1は、第1の実施の形態に係る土壌の浄化装置を示す図であって、(a)は平面図、(b)は縦断面図、(c)は同土壌の浄化装置に係る水路の詳細を示す拡大断面図である。また、図2の(a)〜(c)は、それぞれ第1の実施の形態に係る土壌の浄化方法による各段階を示す縦断面図である。
また、図3は、第2の実施の形態に係る土壌の浄化装置を示す縦断面図であり、図4は、第3の実施の形態に係る土壌の浄化装置を示す縦断面図である。
Preferred embodiments of the present invention will be described with reference to the drawings. In the description, the same reference numerals are used for the same elements, and duplicate descriptions are omitted.
Here, FIG. 1 is a figure which shows the soil purification apparatus which concerns on 1st Embodiment, Comprising: (a) is a top view, (b) is a longitudinal cross-sectional view, (c) is the soil purification apparatus. It is an expanded sectional view showing details of a waterway concerning. Moreover, (a)-(c) of FIG. 2 is a longitudinal cross-sectional view which shows each step by the soil purification method which concerns on 1st Embodiment, respectively.
FIG. 3 is a longitudinal sectional view showing the soil purification apparatus according to the second embodiment, and FIG. 4 is a longitudinal sectional view showing the soil purification apparatus according to the third embodiment.

<第1の実施の形態>
第1の実施の形態(以下、単に「第1実施形態」という場合がある)に係る土壌の浄化装置1は、図1(a)および(b)に示すように、例えば硝酸性窒素からなる汚染物質を含有する土壌を含む領域(以下、単に「汚染領域」という場合がある)に配置された揚水手段10と、この揚水手段10により揚水された地下水W1を浄化する浄化プラント(浄化手段)20と、水分に表面張力低下処理を施す磁場処理機(表面張力低下手段)30と、表面張力低下処理が施された水分を地盤に供給する水分供給手段である水路40とを備えている。なお、浄化対象となる汚染物質は、硝酸性窒素に限定されるものではない。
<First Embodiment>
The soil purification apparatus 1 according to the first embodiment (hereinafter may be simply referred to as “first embodiment”) is made of, for example, nitrate nitrogen as shown in FIGS. 1 (a) and 1 (b). The pumping means 10 disposed in an area including soil containing pollutants (hereinafter sometimes simply referred to as “polluted area”), and a purification plant (purifying means) for purifying the groundwater W1 pumped by the pumping means 10 20, a magnetic field processor (surface tension lowering means) 30 that performs a surface tension reduction process on moisture, and a water channel 40 that is a moisture supply means for supplying the surface subjected to the surface tension reduction process to the ground. The pollutant to be purified is not limited to nitrate nitrogen.

揚水手段10は、汚染領域に形成されて汚染地下水W1を揚水する揚水井11と、揚水井11の上端から浄化プラント20まで揚水した汚染地下水W1を流下可能に配管された汚染水管12と、汚染地下水W1を揚水するために揚水井11に吸引力を付与する揚水ポンプ13と、から構成されている。   The pumping means 10 includes a pumping well 11 that pumps the contaminated groundwater W1 formed in the contaminated area, a contaminated water pipe 12 that is piped so that the contaminated groundwater W1 pumped from the upper end of the pumping well 11 to the purification plant 20 can flow down, In order to pump up the groundwater W1, the pumping pump 13 is configured to provide a suction force to the pumping well 11.

揚水井11は、汚染領域を通過して汚染物質を含有する汚染地下水W1を全て回収することが可能となるように汚染領域内または汚染領域周辺において複数本(本実施形態では9本)配置するものとする。また、揚水井11は、公知の手段により構築すればよく、その構造は限定されるものではないが、本実施形態では、汚染領域の地盤G内に鉛直方向に削孔された縦孔に浄化材が充填された有孔管を配置してなる。   The pumping wells 11 are arranged in a plurality (9 in this embodiment) in or around the contaminated area so as to be able to collect all the contaminated groundwater W1 containing the pollutant through the contaminated area. Shall. Further, the pumping well 11 may be constructed by known means, and the structure thereof is not limited. In this embodiment, the pumping well 11 is purified into a vertical hole drilled in the vertical direction in the ground G of the contaminated area. A perforated tube filled with a material is arranged.

揚水井11の上端には汚染水管12が接続されており、揚水井11の上端の汚染水管12との接続部は図示しないパッカーにより遮蔽されている。
汚染水管12は、浄化プラント20まで配管されており、また、汚染地下水W1を取水するための吸引力を付与するための揚水ポンプ13が接続されている。
A contaminated water pipe 12 is connected to the upper end of the pumping well 11, and a connection portion between the upper end of the pumping well 11 and the contaminated water pipe 12 is shielded by a packer (not shown).
The contaminated water pipe 12 is connected to the purification plant 20, and is connected to a pumping pump 13 for applying a suction force for taking the contaminated groundwater W1.

浄化プラント20は、揚水手段10により揚水された汚染地下水W1を無害化処理して浄化水W2とするものであって、その構成は限定されるものではなく、汚染地下水W1(汚染土壌)が含有する汚染物質の種類や汚染領域の規模などに応じて適宜設定すればよい。   The purification plant 20 detoxifies the contaminated groundwater W1 pumped by the pumping means 10 to obtain purified water W2, and its configuration is not limited, and the contaminated groundwater W1 (contaminated soil) is contained. What is necessary is just to set suitably according to the kind of pollutant to be performed, the scale of a contaminated area, etc.

また、磁場処理機30は、浄化プラント20により無害化処理が施された浄化水W2に磁場処理を施すことにより、浄化水W2の表面張力を低下して地盤Gに浸透しやすい磁場処理水W3を生成するものである。なお、第1実施形態では、表面張力低下手段として、磁場処理機30を採用するものとしたが、水分の表面張力を低下させて、地盤Gへの浸透力を高めることが可能であれば、表面張力低下手段の構成は限定されるものではない。   Further, the magnetic field processor 30 applies magnetic field treatment to the purified water W2 that has been detoxified by the purification plant 20, thereby reducing the surface tension of the purified water W2 and easily penetrating the ground G. Is generated. In the first embodiment, the magnetic field processor 30 is adopted as the surface tension reducing means. However, if the surface tension of moisture can be reduced and the penetration force to the ground G can be increased, The configuration of the surface tension reducing means is not limited.

水路40は、磁場処理機30により磁場処理が施された磁場処理水W3を地盤Gに供給するものであって、図1(c)に示すように、汚染領域の地表面において形成された溝41と、溝41内に配管された有孔管である供給管42と、溝41内において溝41と供給管42との隙間(供給管42の周囲)に充填された砕石43とにより構成されている。
水路40は、汚染領域の全体への磁場処理水W3の供給が可能となるように形成するものとし、第1実施形態では、図1(a)に示すように、井桁状に形成する。
The water channel 40 supplies the magnetic field treated water W3 subjected to the magnetic field treatment by the magnetic field processor 30 to the ground G, and as shown in FIG. 1 (c), a groove formed on the ground surface of the contaminated area. 41, a supply pipe 42 which is a perforated pipe piped in the groove 41, and a crushed stone 43 filled in a gap (around the supply pipe 42) between the groove 41 and the supply pipe 42 in the groove 41. ing.
The water channel 40 is formed so as to be able to supply the magnetic field treated water W3 to the entire contaminated area. In the first embodiment, the water channel 40 is formed in a grid pattern as shown in FIG.

次に、第1実施形態に係る土壌の浄化方法について、図2を参照して説明する。   Next, the soil purification method according to the first embodiment will be described with reference to FIG.

第1実施形態に係る土壌の浄化方法は、(1)汚染領域の汚染地下水W1を揚水する揚水工と、(2)揚水工により揚水された汚染地下水W1を浄化する浄化工と、(3)浄化工において浄化された浄化水W2に磁場処理を施す表面張力低下工と、(4)磁場処理が施された磁場処理水W3を地中に浸透させる注水工と、(5)汚染地下水W1の揚水により低下した地下水位WLを所定の高さまで上昇させる地下水位上昇工とから構成されている。   The soil purification method according to the first embodiment includes (1) a pump that pumps the contaminated groundwater W1 in the contaminated area, (2) a purifier that purifies the contaminated groundwater W1 pumped by the pump, and (3) A surface tension reducing work for applying a magnetic field treatment to the purified water W2 purified by the purification work, (4) a water injection work for infiltrating the magnetically treated water W3 subjected to the magnetic treatment into the ground, and (5) a contaminated groundwater W1. It consists of a groundwater level raising work that raises the groundwater level WL lowered by pumping up to a predetermined height.

(1)揚水工
揚水工では、揚水手段10により地盤G内から汚染地下水W1の揚水を行い、図2(a)に示すように、地盤Gの地層や地下水水量により一定の高さに保たれた自然の地下水位WLが、図2(b)に示す地下水位WLのように、所定の高さに低下するまで連続して行う。
(1) Pumping works In the pumping works, the pumping means 10 pumps the contaminated groundwater W1 from the ground G, and as shown in FIG. 2 (a), it is kept at a constant height by the ground layer and groundwater quantity. Further, the natural groundwater level WL is continuously increased to a predetermined height as in the case of the groundwater level WL shown in FIG.

(2)浄化工
浄化工では、揚水工により地盤Gから取水(揚水)された汚染地下水W1を浄化プラント20により浄化する。
揚水工により揚水された汚染地下水W1は、図2(a)および(b)に示すように、汚染水管12を介して浄化プラント20へと圧送される。そして、浄化プラント20では、汚染地下水W1に無害化処理を施して、浄化水W2を生成する。
(2) Purification Works In the purification works, the purification plant 20 purifies the contaminated groundwater W1 taken (pumped) from the ground G by the pumping works.
As shown in FIGS. 2A and 2B, the contaminated groundwater W1 pumped by the pump is pumped to the purification plant 20 via the contaminated water pipe 12. And in the purification plant 20, the decontamination process is performed to the contaminated ground water W1, and the purified water W2 is produced | generated.

(3)表面張力低下工
表面張力低下工では、浄化工により生成された浄化水W2に磁場処理機30により磁場処理(表面張力低下処理)を施す(図2(a)および(b)参照)。
浄化工において無害化処理が施された汚染地下水W1である浄化水W2は、磁場処理機30に流下されて磁場処理が施される。磁場処理が施された浄化水W2である磁場処理水W3は、表面張力が低下されており、土壌の間隙に浸透しやすい、いわゆる高浸透水である。
(3) Surface tension reduction process In the surface tension reduction process, the magnetic field treatment (surface tension reduction process) is performed on the purified water W2 generated by the purification process by the magnetic field processor 30 (see FIGS. 2A and 2B). .
Purified water W2, which is contaminated groundwater W1 that has been detoxified in the purifier, flows down to the magnetic field processor 30 and is subjected to magnetic field treatment. The magnetically treated water W3, which is the purified water W2 that has been subjected to the magnetic field treatment, is so-called highly osmotic water that has a reduced surface tension and is likely to penetrate into the soil gap.

(4)注水工
注水工では、表面張力低下工により生成された磁場処理水W3を、水分供給手段(水路40)により地盤Gに浸透させる(図2(a)および(b)参照)。
ここで、浄化工、表面張力低下工および注水工は、揚水工と並行して行うものとするが、第1実施形態では、揚水手段10による汚染地下水W1の揚水量が、注水工による磁場処理水W3の浸透水量よりも多いため、図2(b)に示すように、地下水位WLが低下する。また、第1実施形態では、注水工により地盤Gに浸透させる水分として揚水工により揚水された汚染地下水W1を、浄化した後、磁場処理を施した磁場処理水W3を使用するものとしたが、地盤Gに浸透させる水分の供給源は限定されるものではなく、例えば、水道水や河川、湖、海等から採取した水を使用してもよい。
(4) Water filling work In the water filling work, the magnetic field treated water W3 generated by the surface tension reducing work is infiltrated into the ground G by the water supply means (water channel 40) (see FIGS. 2A and 2B).
Here, the purification work, the surface tension reduction work, and the water injection work are performed in parallel with the water pumping work, but in the first embodiment, the pumping amount of the contaminated groundwater W1 by the water pumping means 10 is the magnetic field treatment by the water pouring work. Since it is larger than the amount of osmotic water of the water W3, the groundwater level WL is lowered as shown in FIG. Moreover, in 1st Embodiment, although the contaminated groundwater W1 pumped up by the pumping machine as water to be permeated into the ground G by the water injection work is purified, the magnetic field treated water W3 subjected to the magnetic field treatment is used. The supply source of moisture to be permeated into the ground G is not limited. For example, tap water, water collected from rivers, lakes, seas, or the like may be used.

(5)地下水位上昇工
揚水工により所定の高さまで地下水位WLが低下されたら、揚水手段10による汚染地下水W1の揚水を一旦停止することにより、地盤処理水W3および自然に流入してきた地下水により、図2(c)に示すように地下水位WLを上昇させる。なお、地下水位上昇工では、必ずしも揚水手段10による揚水を停止する必要はなく、例えば、汚染地下水W1の揚水量を低下させて、地盤Gに浸透させる磁場処理水W3の水量を揚水量に比べて多くすることにより地下水位WLを上昇させてもよい。
(5) Groundwater level raising work When the groundwater level WL is lowered to a predetermined height by the pumping works, the pumping of the contaminated groundwater W1 by the pumping means 10 is temporarily stopped, so that the ground treatment water W3 and the groundwater that has flowed in naturally As shown in FIG. 2 (c), the groundwater level WL is raised. In the groundwater level raising work, the pumping by the pumping means 10 is not necessarily stopped. For example, the pumping amount of the contaminated groundwater W1 is reduced, and the amount of the magnetically treated water W3 that permeates the ground G is compared with the pumping amount. The groundwater level WL may be increased by increasing the amount of water.

そして、地下水位WLが所定の水位にまで上昇したら、揚水手段10による揚水を再開する。この作業を繰り返し行うことにより、汚染領域における地下水位WLの低下と上昇とを繰り返し、汚染物質を含有する土壌の洗浄を行う。   And if the groundwater level WL rises to a predetermined water level, the pumping by the pumping means 10 is resumed. By repeating this operation, the groundwater level WL in the contaminated area is repeatedly lowered and raised, and the soil containing the pollutant is washed.

なお、第1実施形態では、揚水井11に吸引力を付与する揚水ポンプ13と連動させることなく、水路40に水分を流下させる構成とすることで、地下水位上昇工において揚水を一旦停止しても、連続して汚染領域への水分の供給を行う(水分を汚染領域に供給する)構成とする。このとき、水路40に供給される水分は、揚水手段10の揚水力と磁場処理水W3の地盤Gへの浸透力により生じる水量の差により図示しない地上の貯水槽に貯留された浄化水W2(磁場処理水W3)や別途採取した水分を使用するものとする。
ここで、揚水ポンプ13と浄化プラント20、磁場処理機30および水路40とを連動させることで、揚水の停止とともに、汚染領域への水路40からの水分の供給も停止して、地下水位上昇工は自然に流入してきた地下水により行う構成としてもよいことはいうまでもない。
In addition, in 1st Embodiment, it is set as the structure which makes water flow down to the water channel 40, without interlock | cooperating with the pumping pump 13 which provides the suction power to the pumping well 11, and temporarily stops pumping in a groundwater level raising work. In addition, the water is continuously supplied to the contaminated area (water is supplied to the contaminated area). At this time, the water supplied to the water channel 40 is purified water W2 stored in a ground water tank (not shown) due to a difference in the amount of water generated by the pumping power of the pumping means 10 and the penetration force of the magnetically treated water W3 into the ground G. It is assumed that magnetically treated water W3) or separately collected water is used.
Here, by interlocking the pumping pump 13 with the purification plant 20, the magnetic field processor 30 and the water channel 40, the supply of water from the water channel 40 to the contaminated area is stopped together with the stoppage of the pumping, and the groundwater level raising work is stopped. Needless to say, the construction may be performed by groundwater that naturally flows in.

以上、第1実施形態の土壌の浄化方法によれば、汚染地下水W1の揚水と磁場処理水W3の注水とを繰り返し行うため、汚染物質を含有する土壌の洗浄を確実に行うことができ、汚染領域に存在する汚染物質を完全に取り除くことができる。   As described above, according to the soil purification method of the first embodiment, since the pumping of the contaminated groundwater W1 and the water injection of the magnetically treated water W3 are repeatedly performed, the soil containing the pollutant can be reliably washed, Contaminants present in the area can be completely removed.

また、揚水量の調整のみで優れた浄化効果を得ることができるため、作業的にも優れている。   Moreover, since an excellent purification effect can be obtained only by adjusting the pumping amount, it is excellent in terms of work.

また、揚水工によって、揚水手段10を介して揚水することにより地下水位WLを低下させた後、地下水位上昇工により再度汚染領域を地下水に浸すため、揚水工において水みちが形成されても、汚染領域全体の汚染物質を地下水に溶出させて、回収することが可能となるため、確実に汚染物質を含有する土壌の洗浄を行うことが可能となる。   In addition, after lowering the groundwater level WL by pumping the water through the pumping means 10 by the pump, the contaminated area is again immersed in the groundwater by the groundwater level raising work. Since it becomes possible to elute and collect the pollutants in the entire contaminated area in the groundwater, it is possible to reliably wash the soil containing the pollutants.

また、注水工による地盤Gへの磁場処理水W3の供給は、汚染領域全体の表面に形成された水路40を介して行うため、汚染領域の上方から磁場処理水W3(洗浄水)を浸透させることで、地下水位WLよりも上にある領域の汚染物質に関しても洗い流し、汚染物質の回収を確実に行うことが可能となる。   Further, since the magnetically treated water W3 is supplied to the ground G by the water injection work through the water channel 40 formed on the entire surface of the contaminated area, the magnetically treated water W3 (cleaning water) is permeated from above the contaminated area. As a result, it is possible to wash away the contaminants in the region above the groundwater level WL and to reliably collect the contaminants.

また、水路40は、溝41内において供給管42に周囲に砕石43が充填されているため、表面積が広く、浸透水(磁場処理水W3)が含有する鉄分等の酸化が原因による膜が形成されることがなく、地盤Gへの水分の供給が妨げられないため、好適である。なお、水路40の構成は前記のものに限定させるものではなく、例えば、供給管42の周囲をヤシ繊維等により被覆することで同様の効果を得る構成としてもよい。   Further, since the water channel 40 is filled with crushed stone 43 around the supply pipe 42 in the groove 41, the surface of the water channel 40 is wide, and a film is formed due to oxidation of iron or the like contained in the permeated water (magnetic field treated water W3). This is preferable because the water supply to the ground G is not hindered. Note that the configuration of the water channel 40 is not limited to that described above, and for example, the same effect may be obtained by covering the periphery of the supply pipe 42 with palm fiber or the like.

また、浄化装置1の構成は、揚水井11、浄化プラント20、磁場処理機30および水路40のみなため、従来の揚水注水方法と同規模であり、新たな用地を確保する必要がなく、好適である。   Moreover, since the structure of the purification apparatus 1 is only the pumping well 11, the purification plant 20, the magnetic field processor 30, and the water channel 40, it is the same scale as the conventional pumping water injection method, and it is not necessary to ensure a new site and is suitable. It is.

また、揚水井11に浄化材が充填しているため、汚染地下水W1の揚水とともに浄化効果を得ることができ、浄化プラント20の簡略化または省略が可能となり、故に、浄化装置1の小規模化が可能となる。   In addition, since the pumping well 11 is filled with the purification material, the purification effect can be obtained together with the pumping of the contaminated groundwater W1, and the purification plant 20 can be simplified or omitted. Is possible.

<第2の実施の形態>
第2の実施の形態(以下、単に「第2実施形態」という場合がある)に係る土壌の浄化装置2は、図3に示すように、汚染物質を含有する土壌を含む領域(以下、単に「汚染領域」という場合がある)に配置された揚水手段10と、この揚水手段10により揚水された地下水W1を浄化する浄化プラント(浄化手段)20と、水分に表面張力低下処理を施す磁場処理機(表面張力低下手段)30と、表面張力低下処理が施された水分を地盤Gに供給する水分供給手段である散水管(散布手段)44とを備えている。
<Second Embodiment>
As shown in FIG. 3, the soil purification apparatus 2 according to the second embodiment (hereinafter may be simply referred to as “second embodiment”) includes a region containing soil containing contaminants (hereinafter simply referred to as “second embodiment”). The pumping means 10 disposed in the “contaminated region”), the purification plant (purifying means) 20 for purifying the groundwater W1 pumped by the pumping means 10, and the magnetic field treatment for subjecting the moisture to a surface tension reduction process Machine (surface tension lowering means) 30 and water sprinkling pipe (spreading means) 44 which is a water supply means for supplying the ground G with water subjected to the surface tension lowering process.

揚水手段10は、汚染領域に形成されて汚染地下水W1を揚水する揚水井11と、揚水井11の上端から浄化プラント20まで揚水した汚染地下水W1を流下可能に配管された汚染水管12と、汚染地下水W1を揚水するために揚水井11に吸引力を付与する揚水ポンプ13と、から構成されている。なお、揚水手段10の詳細は、第1実施形態で説明したものと同様なため、詳細な説明は省略する。   The pumping means 10 includes a pumping well 11 that pumps the contaminated groundwater W1 formed in the contaminated area, a contaminated water pipe 12 that is piped so that the contaminated groundwater W1 pumped from the upper end of the pumping well 11 to the purification plant 20 can flow down, In order to pump up the groundwater W1, the pumping pump 13 is configured to provide a suction force to the pumping well 11. In addition, since the detail of the pumping means 10 is the same as that of what was demonstrated in 1st Embodiment, detailed description is abbreviate | omitted.

浄化プラント20は、揚水手段10により揚水された汚染地下水W1を無害化処理して浄化水W2とするものであって、その構成は限定されるものではなく、汚染地下水W1(汚染土壌)が含有する汚染物質の種類や汚染領域の規模などに応じて適宜設定すればよい。   The purification plant 20 detoxifies the contaminated groundwater W1 pumped by the pumping means 10 to obtain purified water W2, and its configuration is not limited, and the contaminated groundwater W1 (contaminated soil) is contained. What is necessary is just to set suitably according to the kind of pollutant to be performed, the scale of a contaminated area, etc.

また、磁場処理機30は、浄化プラント20により無害化処理が施された浄化水W2に磁場処理を施すことにより、浄化水W2の表面張力を低下して地盤Gに浸透しやすい磁場処理水W3を生成するものである。なお、第2実施形態に係る磁場処理機30は、第1実施形態で説明したものと同様なため、詳細な説明は省略する。   Further, the magnetic field processor 30 applies magnetic field treatment to the purified water W2 that has been detoxified by the purification plant 20, thereby reducing the surface tension of the purified water W2 and easily penetrating the ground G. Is generated. Note that the magnetic field processor 30 according to the second embodiment is the same as that described in the first embodiment, and a detailed description thereof will be omitted.

散水管44は、磁場処理機30により磁場処理が施された磁場処理水W3を地盤Gに供給するものであって、汚染領域の地表面上に配管された有孔管から構成されている。
散水管44は、汚染領域の全体への磁場処理水W3の供給が可能となるように配管するものとする。
The water spray pipe 44 supplies the ground G with the magnetic field treated water W3 that has been subjected to the magnetic field treatment by the magnetic field processor 30, and is composed of a perforated pipe that is piped on the ground surface of the contaminated area.
The sprinkling pipe 44 is piped so that the magnetic field treated water W3 can be supplied to the entire contaminated area.

次に、第2実施形態に係る土壌の浄化方法について、図3を参照して説明する。
第2実施形態に係る土壌の浄化方法は、(1)汚染領域の汚染地下水W1を揚水する揚水工と、(2)揚水工により揚水された汚染地下水W1を浄化する浄化工と、(3)浄化工により浄化された浄化水W2に磁場処理を施す表面張力低下工と、(4)磁場処理が施された磁場処理水W3を地中に浸透させる注水工と、から構成されている。
Next, the soil purification method according to the second embodiment will be described with reference to FIG.
The soil purification method according to the second embodiment includes: (1) a pump that pumps the contaminated groundwater W1 in the contaminated area; (2) a purifier that purifies the contaminated groundwater W1 pumped by the pump; and (3) It consists of a surface tension lowering work for applying a magnetic field treatment to the purified water W2 purified by the purification work, and (4) a water injection work for infiltrating the magnetically treated water W3 subjected to the magnetic field treatment into the ground.

(1)揚水工
揚水工では、揚水手段10による汚染領域の汚染地下水W1の揚水を、浄化プラント20による処理能力や、散水管44により散水された磁場処理水W3の地盤Gへの浸透力等に応じた揚水量により連続的に行う。
(1) Pumping works In the pumping works, the treatment capacity of the contaminated groundwater W1 in the contaminated area by the pumping means 10 is treated by the purification plant 20, the permeability of the magnetically treated water W3 sprinkled by the sprinkling pipe 44 to the ground G, etc. Continuously with the amount of pumping according to.

(2)浄化工
浄化工では、揚水工により地盤Gから取水(揚水)された汚染地下水W1を浄化プラント20により無害化する。
揚水工により揚水された汚染地下水W1は、汚染水管12を介して浄化プラント20へと搬送される。浄化プラント20では、汚染地下水W1に無害化処理が施して、浄化水W2を生成する。
(2) Purification Plant In the purification plant, the purification plant 20 renders the contaminated groundwater W1 taken (ground) from the ground G by the pumping plant harmless.
The contaminated groundwater W1 pumped by the pump is transferred to the purification plant 20 through the contaminated water pipe 12. In the purification plant 20, the contaminated groundwater W1 is detoxified to generate purified water W2.

(3)表面張力低下工
表面張力低下工では、浄化工により生成された浄化水W2に磁場処理機30により磁場処理を施す。
浄化工により無害化処理が施された汚染地下水W1である浄化水W2は、磁場処理機30に流下されて磁場処理が施される。磁場処理が施された浄化水W2である磁場処理水W3は、表面張力が低下されており、土壌の間隙に浸透しやすい、いわゆる高浸透水である。
(3) Surface tension lowering work In the surface tension lowering work, the magnetic field treatment machine 30 subjects the purified water W2 generated by the purification work to a magnetic field treatment.
Purified water W2, which is contaminated groundwater W1 that has been detoxified by the purifier, flows down to the magnetic field processor 30 and is subjected to magnetic field treatment. The magnetically treated water W3, which is the purified water W2 that has been subjected to the magnetic field treatment, is so-called highly osmotic water that has a reduced surface tension and is likely to penetrate into the soil gap.

(4)注水工
注水工では、表面張力低下工により磁場処理が施された磁場処理水W3を、散水管44を介して汚染領域の地表面に散布して、地盤G内に浸透させる。
(4) Water filling work In the water filling work, the magnetic field treated water W3 that has been subjected to the magnetic field treatment by the surface tension reducing work is sprayed on the ground surface of the contaminated area through the water spray pipe 44 and penetrated into the ground G.

揚水工、浄化工、表面張力低下工および注水工は、地下水位WLが維持されるように、並行して行われる。   The pumping work, the purification work, the surface tension reduction work and the water pouring work are performed in parallel so that the groundwater level WL is maintained.

以上、第2実施形態に係る土壌の浄化方法によれば、汚染領域内において、水分(地下水)を循環させることにより、汚染物質を含有する土壌を連続的に洗浄するとともに、地下水に汚染物質を溶出させた後回収するため、確実に土壌の浄化を行うことを可能としている。   As described above, according to the soil purification method according to the second embodiment, the soil containing the pollutant is continuously washed by circulating water (groundwater) in the contaminated area, and the pollutant is introduced into the groundwater. Since it is recovered after elution, it is possible to reliably clean up the soil.

また、汚染物質を含有した汚染地下水W1は、浄化プラント20において無害化処理がなされた後、随時地盤Gに戻されるため、地下水位が低下することによる地盤沈下等が生じることがない。そのため、生態系に影響を及ぼすことが無く、好適である。   Moreover, since the contaminated groundwater W1 containing the pollutant is detoxified in the purification plant 20 and then returned to the ground G as needed, ground subsidence due to a decrease in the groundwater level does not occur. Therefore, it does not affect the ecosystem and is preferable.

また、汚染領域は地下水により常時浸されているため、汚染物質を地下水に溶出されて、完全に除去することが可能となる。   In addition, since the contaminated area is constantly immersed in groundwater, the contaminants are eluted in the groundwater and can be completely removed.

また、散水管44による水分(磁場処理水W3)の供給を、地表面から行うため、地下水位WL以高の地盤G内に存在する汚染物質に関しても、この浸透水に溶出させて回収することができ、土壌の浄化を確実に行うことができる。   In addition, since the water (magnetic field treated water W3) is supplied from the ground surface by the water spray pipe 44, contaminants existing in the ground G higher than the groundwater level WL are also eluted and collected in the permeated water. The soil can be reliably purified.

<第3の実施の形態>
第3の実施の形態(以下、単に「第3実施形態」という場合がある)に係る土壌の浄化装置3は、図4に示すように、汚染物質を含有する土壌を含む領域(以下、単に「汚染領域」という場合がある)に配置された揚水手段10と、この揚水手段10により揚水された地下水W1を浄化する浄化プラント(浄化手段)20と、水分に表面張力低下処理を施す磁場処理機(図示省略)と、表面張力低下処理が施された水分を地盤Gに供給する水分供給手段である注水井45とを備えている。
<Third Embodiment>
As shown in FIG. 4, the soil purification apparatus 3 according to the third embodiment (hereinafter may be simply referred to as “third embodiment”) includes a region containing soil containing contaminants (hereinafter simply referred to as “third embodiment”). The pumping means 10 disposed in the “contaminated region”), the purification plant (purifying means) 20 for purifying the groundwater W1 pumped by the pumping means 10, and the magnetic field treatment for subjecting the moisture to a surface tension reduction process And a water injection well 45 which is a water supply means for supplying the ground G with the water subjected to the surface tension lowering process.

揚水手段10は、汚染領域に形成されて汚染地下水W1を揚水する揚水井11と、揚水井11の上端から浄化プラント20まで揚水した汚染地下水W1を流下可能に配管された汚染水管12と、汚染地下水W1を揚水するために揚水井11に吸引力を付与する揚水ポンプ13と、から構成されている。なお、揚水手段10の詳細は、第1実施形態で説明したものと同様なため、詳細な説明は省略する。   The pumping means 10 includes a pumping well 11 that pumps the contaminated groundwater W1 formed in the contaminated area, a contaminated water pipe 12 that is piped so that the contaminated groundwater W1 pumped from the upper end of the pumping well 11 to the purification plant 20 can flow down, In order to pump up the groundwater W1, the pumping pump 13 is configured to provide a suction force to the pumping well 11. In addition, since the detail of the pumping means 10 is the same as that of what was demonstrated in 1st Embodiment, detailed description is abbreviate | omitted.

浄化プラント20は、揚水手段10により揚水された汚染地下水W1を無害化処理して浄化水W2とするものであって、その構成は限定されるものではなく、汚染地下水W1(汚染土壌)が含有する汚染物質の種類や汚染領域の規模などに応じて適宜設定すればよい。   The purification plant 20 detoxifies the contaminated groundwater W1 pumped by the pumping means 10 to obtain purified water W2, and its configuration is not limited, and the contaminated groundwater W1 (contaminated soil) is contained. What is necessary is just to set suitably according to the kind of pollutant to be performed, the scale of a contaminated area, etc.

また、磁場処理機は、浄化プラント20と注水ポンプ46との間に配置されて、浄化プラント20により無害化処理が施された浄化水W2に磁場処理を施すことにより、浄化水W2の表面張力を低下して地盤Gに浸透しやすい磁場処理水を生成するものである。なお、第3実施形態に係る磁場処理機は、第1実施形態で説明したものと同様なため、詳細な説明は省略する。   Further, the magnetic field processor is disposed between the purification plant 20 and the water injection pump 46, and performs a magnetic field treatment on the purified water W2 that has been detoxified by the purification plant 20, so that the surface tension of the purified water W2 is increased. Is generated, and magnetically treated water that easily penetrates into the ground G is generated. The magnetic field processor according to the third embodiment is the same as that described in the first embodiment, and thus detailed description thereof is omitted.

注水井45は、注水ポンプ46を介して圧送された磁場処理機により磁場処理が施された磁場処理水(浄化水W2)を地盤Gに供給する井戸であって、汚染領域に複数形成されている。
なお、注水井45の配置は限定されるものではないが、汚染領域の全体への磁場処理水(浄化水W2)の供給が可能となるように配置するものとする。
The water injection well 45 is a well that supplies the ground G with magnetic field treated water (purified water W2) that has been subjected to magnetic field treatment by a magnetic field treatment machine that is pumped through the water injection pump 46, and a plurality of wells are formed in the contaminated area. Yes.
In addition, although arrangement | positioning of the water injection well 45 is not limited, it shall arrange | position so that supply of the magnetic field treated water (purified water W2) to the whole contamination area | region is attained.

ここで、第3実施形態に係る浄化装置3を利用した土壌の浄化方法は、第1実施形態に示した土壌の浄化方法と同様なため、詳細な説明は省略する。
また、第3実施形態に係る浄化装置3および土壌の浄化方法により得られる作用効果は、第1実施形態で示した内容と同様なため、詳細な説明は省略する。
Here, since the soil purification method using the purification device 3 according to the third embodiment is the same as the soil purification method shown in the first embodiment, detailed description thereof is omitted.
Moreover, since the effect acquired by the purification apparatus 3 and the soil purification method which concern on 3rd Embodiment is the same as the content shown in 1st Embodiment, detailed description is abbreviate | omitted.

以上、本発明について、好適な実施形態について説明した。しかし、本発明は、前述の各実施形態に限られず、前記の各構成要素については、本発明の趣旨を逸脱しない範囲で、適宜設計変更が可能であることはいうまでもない。
例えば、第1実施形態において、地下水位の低下および上昇を繰り返す際に、当該地下水位を、毎回変化させることにより、地盤内を流れる地下水の水みちを変化させることにより土壌の洗浄効果を高める構成としてもよい。同様に、汚染地下水の揚水量や磁場処理水の供給量を随時変化させることにより、土壌の洗浄効果を高めるものとしてもよい。
The preferred embodiments of the present invention have been described above. However, the present invention is not limited to the above-described embodiments, and it goes without saying that the above-described constituent elements can be appropriately changed in design without departing from the spirit of the present invention.
For example, in 1st Embodiment, when repeating a fall and rise of a groundwater level, the said groundwater level is changed every time, The structure which improves the washing | cleaning effect of soil by changing the water path of the groundwater which flows in the ground It is good. Similarly, it is good also as what improves the washing | cleaning effect of soil by changing the amount of pumping of contaminated groundwater and the supply amount of magnetically treated water at any time.

また、前記各実施形態において、揚水された汚染地下水は、必ずしも地盤に戻す必要はなく、例えば浄化プラントにより浄化処理を施した後、河川等に放流してもよい。
また、第1実施形態に係る地下水上昇工の地下水位の上昇は、汚染領域に自然に流入してきた地下水により行われることも可能であることはいうまでもない。
In each of the above embodiments, the pumped contaminated groundwater does not necessarily have to be returned to the ground. For example, after the purification process is performed by a purification plant, it may be discharged into a river or the like.
Needless to say, the increase in the groundwater level of the groundwater riser according to the first embodiment can be performed by the groundwater that naturally flows into the contaminated area.

また、前記各実施形態では、揚水井として、浄化材が充填されたものを使用するものとしたが、揚水井に必ずしも浄化材が充填されている必要はないことはいうまでもない。
また、汚染領域に供給される水分に汚染物質の除去に効果的な物質や薬剤等をあらかじめ混合しておくことにより、土壌の浄化を早める構成にしてもよい。
Moreover, in each said embodiment, although the thing filled with the purification material was used as a pumping well, it cannot be overemphasized that the purification material does not necessarily need to be filled with the pumping well.
In addition, the soil may be accelerated by preliminarily mixing a substance or a drug effective for removing the pollutant with the moisture supplied to the contaminated area.

また、前記各実施形態では、水路または散水管と注水井とを個別に設ける形態について説明したが、水分供給手段として、水路または散水管と注水井とを並存させてもよいことはいうまでもない。
また、前記各実施形態では、磁場処理機により地盤に浸透させる水分に表面張力低下処理を施す構成としたが、必ずしも水分に表面張力低下処理を施す必要がないことはいうまでもない。
さらに、本発明に係る水分供給手段の構成は、前記各実施形態に示した水路、散水管、注水井に限定されるものではなく、適宜設定すればよい。
Moreover, in each said embodiment, although the form which provides a waterway or a sprinkling pipe and a water injection well separately was demonstrated, it cannot be overemphasized that a waterway or a watering pipe and a water injection well may coexist as a water supply means. Absent.
Moreover, in each said embodiment, it was set as the structure which performs the surface tension reduction process to the water | moisture content penetrate | infiltrated into the ground with a magnetic field processor, but it cannot be overemphasized that it is not necessarily necessary to perform the surface tension reduction process to a water | moisture content.
Furthermore, the structure of the water supply means according to the present invention is not limited to the water channel, the water spray pipe, and the water injection well shown in the above embodiments, and may be set as appropriate.

第1の実施の形態に係る土壌の浄化装置を示す図であって、(a)は平面図、(b)は縦断面図、(c)は水路の詳細を示す拡大断面図である。It is a figure which shows the purification apparatus of the soil which concerns on 1st Embodiment, (a) is a top view, (b) is a longitudinal cross-sectional view, (c) is an expanded sectional view which shows the detail of a water channel. (a)〜(c)は、それぞれ第1の実施の形態に係る土壌の浄化方法による各段階を示す縦断面図である。(A)-(c) is a longitudinal cross-sectional view which shows each step by the purification method of the soil which concerns on 1st Embodiment, respectively. 第2の実施の形態に係る土壌の浄化装置を示す縦断面図である。It is a longitudinal cross-sectional view which shows the purification apparatus of the soil which concerns on 2nd Embodiment. 第3の実施の形態に係る土壌の浄化装置を示す縦断面図である。It is a longitudinal cross-sectional view which shows the purification apparatus of the soil which concerns on 3rd Embodiment.

符号の説明Explanation of symbols

1,2,3 浄化装置
10 揚水手段
11 揚水井
20 浄化プラント(浄化手段)
30 磁場処理機(表面張力低下手段)
40 水路
44 散水管(散布手段)
45 注水井(水分供給手段)
G 地盤
WL 地下水位
W1 汚染地下水
W2 浄化水
W3 磁場処理水
1, 2, 3 Purification device 10 Pumping means 11 Pumping well 20 Purification plant (purifying means)
30 Magnetic field treatment machine (means for reducing surface tension)
40 water channels 44 watering pipes (dispersing means)
45 Injection well (moisture supply means)
G Ground WL Groundwater level W1 Contaminated groundwater W2 Purified water W3 Magnetically treated water

Claims (11)

地下水を利用して汚染物質を含有する土壌を洗浄する土壌の浄化方法であって、
汚染領域の地下水を揚水して地下水の水位を低下させた後、前記地下水の揚水により低下した地下水の水位を上昇させることを繰り返し行うことを特徴とする、土壌の浄化方法。
A soil purification method for cleaning soil containing pollutants using groundwater,
A method for purifying soil, comprising: pumping up groundwater in a contaminated area to lower the level of groundwater and then repeatedly raising the level of groundwater lowered by pumping the groundwater.
前記汚染領域に水分を供給することを特徴とする、請求項1に記載の土壌の浄化方法。   The soil purification method according to claim 1, wherein moisture is supplied to the contaminated area. 前記水分を、地表面から浸透させることにより供給することを特徴とする、請求項2に記載の土壌の浄化方法。   The soil purification method according to claim 2, wherein the moisture is supplied by permeating from the ground surface. 前記水分が、前記揚水された地下水を浄化した浄化水であることを特徴とする、請求項2または請求項3に記載の土壌の浄化方法。   4. The soil purification method according to claim 2, wherein the moisture is purified water obtained by purifying the pumped ground water. 前記水分に、表面張力低下処理を施すことを特徴とする、請求項2乃至請求項4のいずれか1項に記載の土壌の浄化方法。   The soil purification method according to any one of claims 2 to 4, wherein the moisture is subjected to a surface tension reduction treatment. 地下水を利用して汚染物質を含有する土壌を洗浄する土壌の浄化方法であって、
汚染領域の地下水を揚水するとともに、地表面から前記汚染領域に水分を浸透させることを特徴とする、土壌の浄化方法。
A soil purification method for cleaning soil containing pollutants using groundwater,
A soil purification method characterized by pumping groundwater in a contaminated area and allowing water to permeate into the contaminated area from the ground surface.
前記水分が、前記揚水された地下水を浄化した浄化水であることを特徴とする、請求項6に記載の土壌の浄化方法。   The soil purification method according to claim 6, wherein the moisture is purified water obtained by purifying the pumped groundwater. 前記水分に、表面張力低下処理を施すことを特徴とする、請求項6または請求項7に記載の土壌の浄化方法。   The soil purification method according to claim 6 or 7, wherein a surface tension lowering treatment is performed on the moisture. 汚染物質を含有する土壌を含む汚染領域に配置された揚水手段と、
前記揚水手段により揚水された地下水を浄化する浄化手段と、
水分に表面張力低下処理を施す表面張力低下手段と、
前記表面張力低下手段により表面張力低下処理が施された水分を前記汚染領域に供給する水分供給手段と、を備えることを特徴とした、土壌の浄化装置。
Pumping means located in a contaminated area including soil containing pollutants;
Purification means for purifying groundwater pumped by the pumping means;
Surface tension lowering means for applying a surface tension lowering treatment to moisture;
A soil purification apparatus comprising: moisture supply means for supplying moisture that has been subjected to surface tension reduction treatment by the surface tension reduction means to the contaminated area.
前記水分供給手段が、地表面に形成された水路であることを特徴とする、請求項9に記載の土壌の浄化装置。   The soil purification apparatus according to claim 9, wherein the moisture supply means is a water channel formed on a ground surface. 前記水分供給手段が、地表面に前記水分を散布する散布手段であることを特徴とする、請求項9に記載の土壌の浄化装置。   The soil purification apparatus according to claim 9, wherein the moisture supply means is a spraying means for spraying the moisture onto the ground surface.
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2014094362A (en) * 2012-11-12 2014-05-22 Uerushii:Kk Operation support system and operation support method for groundwater clarification apparatus
JP2017023915A (en) * 2015-07-17 2017-02-02 鹿島建設株式会社 System and method for preventing clogging
JP2018075527A (en) * 2016-11-09 2018-05-17 株式会社竹中工務店 Soil purification system
JPWO2018043507A1 (en) * 2016-08-29 2019-07-04 株式会社竹中工務店 Underground soil remediation method
CN110255638A (en) * 2019-07-25 2019-09-20 中冶南方都市环保工程技术股份有限公司 A kind of polluted underground water containing nonaqueous phase liquid original position pump-and-treat system system and method

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06193040A (en) * 1992-12-28 1994-07-12 Kajima Corp Purifying method of contaminated soil
JPH10258266A (en) * 1997-03-18 1998-09-29 Shimizu Corp Method for repairing original position of polluted ground and pollutant treatment apparatus
JP2000051834A (en) * 1998-08-11 2000-02-22 Hazama Gumi Ltd Method for remedying polluted soil
JP2001017954A (en) * 1999-07-05 2001-01-23 Chiyoda Corp Method for cleaning polluted soil
JP2001225054A (en) * 2000-02-15 2001-08-21 Kajima Corp Method and system for cleaning contaminated soil
JP2003164844A (en) * 2001-11-29 2003-06-10 Ohbayashi Corp Construction method for washing contaminated soil by penetrating water in situ

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06193040A (en) * 1992-12-28 1994-07-12 Kajima Corp Purifying method of contaminated soil
JPH10258266A (en) * 1997-03-18 1998-09-29 Shimizu Corp Method for repairing original position of polluted ground and pollutant treatment apparatus
JP2000051834A (en) * 1998-08-11 2000-02-22 Hazama Gumi Ltd Method for remedying polluted soil
JP2001017954A (en) * 1999-07-05 2001-01-23 Chiyoda Corp Method for cleaning polluted soil
JP2001225054A (en) * 2000-02-15 2001-08-21 Kajima Corp Method and system for cleaning contaminated soil
JP2003164844A (en) * 2001-11-29 2003-06-10 Ohbayashi Corp Construction method for washing contaminated soil by penetrating water in situ

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2014094362A (en) * 2012-11-12 2014-05-22 Uerushii:Kk Operation support system and operation support method for groundwater clarification apparatus
JP2017023915A (en) * 2015-07-17 2017-02-02 鹿島建設株式会社 System and method for preventing clogging
JPWO2018043507A1 (en) * 2016-08-29 2019-07-04 株式会社竹中工務店 Underground soil remediation method
JP2018075527A (en) * 2016-11-09 2018-05-17 株式会社竹中工務店 Soil purification system
CN110255638A (en) * 2019-07-25 2019-09-20 中冶南方都市环保工程技术股份有限公司 A kind of polluted underground water containing nonaqueous phase liquid original position pump-and-treat system system and method

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