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JP7660434B2 - Contaminated soil remediation method - Google Patents
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JP7660434B2 - Contaminated soil remediation method - Google Patents

Contaminated soil remediation method Download PDF

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JP7660434B2
JP7660434B2 JP2021087541A JP2021087541A JP7660434B2 JP 7660434 B2 JP7660434 B2 JP 7660434B2 JP 2021087541 A JP2021087541 A JP 2021087541A JP 2021087541 A JP2021087541 A JP 2021087541A JP 7660434 B2 JP7660434 B2 JP 7660434B2
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contaminated soil
soil
borehole
diffusion
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JP2022180829A (en
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純一 山野辺
忠輔 和田
進 上沢
克也 高柳
久美子 島田
憲俊 石川
達也 塩谷
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Chemical Grouting Co Ltd
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Description

本発明は、例えば揮発性有機化合物(VOC)などの有害化学物質で汚染された土壌を浄化する汚染土壌浄化方法に関するものである。 The present invention relates to a method for purifying contaminated soil, for example soil contaminated with harmful chemicals such as volatile organic compounds (VOCs).

従来、浄化剤を注入しても拡散しにくいような透水性の低い土壌を浄化する技術として、水素を分子拡散によって浸透させ、脱塩素菌の還元的脱塩素化反応により、有害化学物質を生分解する技術が知られている。より詳しくは、例えば、汚染された土壌に形成したボーリング孔に、先端に噴射装置を設けたロッドを挿入し、微生物活性剤を噴射して土壌を切削し、土壌と微生物活性剤が混合された円板状や円錐面状などの混合領域を形成することによって、微生物活性剤の生分解反応により水素を発生させる。発生した水素が分子拡散によって浸透すると、脱塩素菌の還元的脱塩素化反応によって有害化学物質を生分解することができる(例えば、特許文献1参照。)。 A conventional technique for purifying soil with low permeability, where a purification agent is unlikely to diffuse even when injected, is to allow hydrogen to penetrate by molecular diffusion and biodegrade harmful chemicals by the reductive dechlorination reaction of dechlorinating bacteria. More specifically, for example, a rod with an injection device at its tip is inserted into a borehole formed in contaminated soil, and a microbial activator is injected to cut the soil, forming a mixed area such as a disk or cone shape where the soil and microbial activator are mixed, thereby generating hydrogen through the biodegradation reaction of the microbial activator. When the generated hydrogen penetrates by molecular diffusion, harmful chemicals can be biodegraded by the reductive dechlorination reaction of the dechlorinating bacteria (see, for example, Patent Document 1).

特開2015-071126号公報JP 2015-071126 A

上記のようにボーリング、および混合領域の形成によって広い面積の土壌を浄化する場合、円板状などの混合領域を複数形成する必要がある。そして、浄化しようとする領域全域に亘って水素を拡散させるためには、必然的に、複数の円板状などの混合領域による水素の拡散領域が重複する領域が生じることになる。それゆえ、ボーリング、および混合領域の数を低減するなどして作業効率を向上させることが困難であった。 When purifying a large area of soil by boring and forming mixing areas as described above, it is necessary to form multiple mixing areas, such as disk-shaped areas. In order to diffuse hydrogen throughout the entire area to be purified, it is inevitable that there will be areas where the hydrogen diffusion areas caused by multiple mixing areas, such as disk-shaped areas, overlap. This makes it difficult to improve work efficiency by reducing the number of borings and mixing areas.

本発明は、上記の点に鑑みてなされたものであり、水素等の分子拡散によって土壌を浄化する場合の作業効率を向上させ得るようにすることを目的としている。 The present invention was made in consideration of the above points, and aims to improve the work efficiency when purifying soil by molecular diffusion of hydrogen, etc.

上記の目的を達成するために、
本発明は、
汚染された土壌を浄化する汚染土壌浄化方法であって、
ボーリング孔を形成するボーリング孔形成工程と、
上記ボーリング孔に噴射装置を挿入して回転させながら水を高圧で噴射して土壌における面状でスリット状の領域を切削し、浄化剤を圧入・充填することにより、土壌と浄化剤とが混合された混合領域、および上記混合領域の周囲に所定の物質が分子拡散する拡散領域を形成する領域形成工程と、
を有し、
上記領域形成工程は、形成される複数の拡散領域が非円弧状の境界を有し、互いに接し、または重なり合って隣り合うように行われることを特徴とする。
In order to achieve the above objectives,
The present invention relates to
A method for remediating contaminated soil, comprising:
a borehole forming step of forming a borehole;
a region forming process in which an injection device is inserted into the borehole, and while rotating, water is injected at high pressure to cut a planar, slit-shaped region in the soil, and the purification agent is then injected and filled to form a mixed region in which the soil and the purification agent are mixed, and a diffusion region in which a predetermined substance diffuses molecularly around the mixed region;
having
The region forming step is characterized in that the plurality of diffusion regions formed have non-arcuate boundaries and are adjacent to each other and in contact with or overlap each other.

これにより、隣り合う拡散領域の重なり代を小さく抑え、ボーリングの回数を低減したり領域形成工程の効率を向上させたりすることが容易にできる。 This makes it easy to keep the overlap between adjacent diffusion regions small, reduce the number of drilling operations, and improve the efficiency of the region formation process.

本発明では、水素等の分子拡散によって土壌を浄化する場合の作業効率を向上させることができる。 The present invention can improve the work efficiency when purifying soil by molecular diffusion of hydrogen, etc.

噴射装置の例を模式的に示す斜視図である。FIG. 1 is a perspective view showing a schematic example of an injection device. 敷地内の単位浄化区画の例を示す説明図である。FIG. 2 is an explanatory diagram showing an example of a unit purification section within a site. 単位浄化区画内のボーリングごとの浄化領域の形状および配置の例を示す説明図である。FIG. 1 is an explanatory diagram showing an example of the shape and arrangement of purification areas for each borehole within a unit purification section. 混合領域の検出の例を示す説明図である。FIG. 11 is an explanatory diagram showing an example of detection of a mixed region. 単位浄化区画内を複数の円板状の浄化領域によって浄化する場合の浄化領域の配置の例を示す対比例の説明図である。FIG. 13 is an explanatory diagram of a comparative example showing an example of the arrangement of purification regions when a unit purification section is purified by a plurality of disk-shaped purification regions.

以下、本発明の実施形態を図面に基づいて詳細に説明する。 The following describes in detail an embodiment of the present invention with reference to the drawings.

(噴射装置102の概略構成)
まず、図1を参照して、汚染土壌の浄化に用いられる噴射装置102の概略構成について説明する。噴射装置102には、噴射装置102の中心軸に対して点対称となる1対の放射方向に噴流Jを噴射するノズル102aが設けられている。この噴射装置102は、ボーリングロッド101の先端に取り付けられて、予め削孔されたボーリング孔に挿入され、定速で回転させながら、水を高圧で噴射させることにより、土壌における例えば円板Sのように面状でスリット状の領域を切削し、微生物活性剤(浄化剤)を該スリットに圧入・充填することで、土壌と浄化剤とが混合された混合領域を形成し得るようになっている。また、回転速度を回転角に応じて所定に制御したり、高圧水の噴射速度や、噴射圧力、噴射流量を変化させたりすることにより、例えば特許5649052号公報の図12、およびその関連箇所に記載されているように正方形に近い平面形状などの混合領域を形成することもできるようになっている。ここで、上記「面」は、数学におけるように厚さが0である面を意味するのではなく、広がりの大きさに対して厚さが十分に薄い形状であることを意味する。また、上記回転は、回転速度を回転角に応じて変化させながら回転させることや、間欠的な回転、正逆回転を繰り返す回転など、中心軸回りに回る動きを伴う動作を含み得る。
(Schematic configuration of the ejection device 102)
First, referring to FIG. 1, the schematic configuration of an injection device 102 used for purifying contaminated soil will be described. The injection device 102 is provided with a nozzle 102a for injecting jets J in a pair of radial directions that are point symmetrical with respect to the central axis of the injection device 102. The injection device 102 is attached to the tip of a boring rod 101 and inserted into a borehole that has been drilled in advance. While rotating at a constant speed, the injection device 102 injects water at high pressure to cut a planar, slit-shaped area in the soil, for example, like a disk S, and pressurizes and fills the slit with a microbial activator (purifying agent), thereby forming a mixed area in which the soil and the purifying agent are mixed. In addition, by controlling the rotation speed to a predetermined value according to the rotation angle, or by changing the injection speed, injection pressure, and injection flow rate of the high-pressure water, it is possible to form a mixed area such as a planar shape close to a square, as described in, for example, FIG. 12 of Japanese Patent Publication No. 5649052 and related parts thereof. Here, the above-mentioned "surface" does not mean a surface with a thickness of 0 as in mathematics, but means a shape with a thickness that is sufficiently thin compared to the size of the spread. The rotation may include an operation involving a rotational movement around a central axis, such as rotating while changing the rotation speed according to the rotation angle, intermittent rotation, or repeated forward and reverse rotation.

(浄化処理の概要)
水素等の分子拡散による土壌の浄化について説明する。
(Overview of purification process)
This section explains the purification of soil by molecular diffusion of hydrogen and other gases.

上記のような噴射装置102を用い、浄化剤としての微生物活性剤を噴射して、土壌と混合された混合領域を形成することにより、地中に存在する微生物を活性化し、微生物活性剤の生分解反応により水素を発生させることができる。そのような微生物活性剤としては、例えば、窒素、リン、ビタミンB12(コバラミン)の少なくとも1つや、ショ糖脂肪酸エステル、グリセリン、大豆油、水などを含むものを用いることができる。 By using the above-mentioned injection device 102 to inject a microbial activator as a purification agent and form a mixed area in which it is mixed with the soil, it is possible to activate microorganisms present in the ground and generate hydrogen through a biodegradation reaction of the microbial activator. Such microbial activators can include, for example, at least one of nitrogen, phosphorus, and vitamin B12 (cobalamin), or sucrose fatty acid esters, glycerin, soybean oil, water, etc.

発生した水素は分子拡散により難透水層であっても比較的容易に透過し、上記混合領域の周囲に浸透して拡散領域が形成される。そこで、土壌中に存在して有害化学物質(例えば有機塩素化合物)を生分解する性質を有する微生物、例えばデハロ菌(Dehalococcoides属細菌)等の脱塩素菌が活性化して、増殖し、還元的脱塩素化反応により有害化学物質(有機塩素化合物等)が生分解され、土壌が浄化される。 The hydrogen generated penetrates relatively easily through low-permeability layers due to molecular diffusion, and permeates around the mixed region, forming a diffusion region. There, microorganisms that exist in the soil and have the ability to biodegrade harmful chemicals (e.g., organic chlorine compounds), such as dechlorinating bacteria such as Dehalococcoides bacteria, become activated and grow, and the harmful chemicals (e.g., organic chlorine compounds) are biodegraded by reductive dechlorination reactions, purifying the soil.

(浄化領域の具体例)
浄化処理は、具体的には、例えば、図2に示すような浄化対象敷地境界201内において、10m区画ライン202によって区画される10m四方の単位浄化区画ごとに汚染の有無や程度などが判別され、汚染土壌エリア203とされた領域に対して浄化処理が行われる。各汚染土壌エリア203は、それぞれ、例えば図3に示すように16本のボーリング孔303を形成するボーリング孔形成工程と、土壌と浄化剤とが混合された混合領域301、および上記混合領域の周囲に所定の気体が分子拡散する拡散領域302を形成する領域形成工程とが行われることにより浄化される。
(Specific examples of purification areas)
Specifically, for example, within a boundary 201 of a site to be purified as shown in Fig. 2, the presence or absence and the degree of contamination are determined for each 10m square unit purification section divided by 10m division lines 202, and purification is performed on the area determined as a contaminated soil area 203. Each contaminated soil area 203 is purified by carrying out a borehole formation process of forming 16 boreholes 303 as shown in Fig. 3, and a region formation process of forming a mixing region 301 in which soil and a purification agent are mixed, and a diffusion region 302 in which a predetermined gas diffuses molecularly around the above-mentioned mixing region.

上記混合領域301は、ボーリング孔303を中心とした正方形状などの矩形状に形成され、縦横に配置される。また、そのような混合領域301の周囲に水素等が分子拡散することによって、拡散領域302も概ね正方形状に形成される。ここで、上記混合領域301や拡散領域302の正方形状の意義は、必ずしも幾何学的に正確な正方形を意味するのではなく、例えば上記特許5649052号公報の図12等に示されるように各辺が非円弧状、すなわち円弧よりも直線に近い形状であることを意味し、これによって、複数の拡散領域302が図3に2点鎖線で示すように非円弧状の境界を介して隣り合うようになり、拡散領域の境界が円弧状となる場合よりも重なり代を小さく抑え、領域形成工程の効率を容易に向上させることができる。また、汚染土壌エリア203の外側に混合領域301が広がるのを防止、または低減することが容易にできる。 The mixing area 301 is formed in a rectangular shape, such as a square shape, with the borehole 303 at the center, and is arranged vertically and horizontally. In addition, the diffusion area 302 is also formed in a roughly square shape by molecular diffusion of hydrogen and the like around the mixing area 301. Here, the meaning of the square shape of the mixing area 301 and the diffusion area 302 does not necessarily mean a geometrically accurate square, but means that each side is non-arc-shaped, that is, a shape closer to a straight line than an arc, as shown in, for example, FIG. 12 of the above-mentioned Patent Publication No. 5649052. As a result, multiple diffusion areas 302 are adjacent to each other through a non-arc-shaped boundary as shown by the two-dot chain line in FIG. 3, and the overlapping area is kept smaller than when the boundary of the diffusion area is arc-shaped, and the efficiency of the area formation process can be easily improved. In addition, it is easy to prevent or reduce the spread of the mixing area 301 outside the contaminated soil area 203.

ここで、幾何学的に、互いに隣接する4つの混合領域301の頂点の間の部分には、各頂点からの距離が、各混合領域301の辺と拡散領域302の辺との間の距離よりも長くなることから、この各頂点からの距離を分子拡散の距離と考える。この場合、各混合領域301の辺と拡散領域302の辺との間においては水素等の分子拡散範囲は計画領域を超えることとなるが汚染を拡散させることとならず、汚染土壌エリア203内の全域に亘って、拡散領域302による浄化を十分、適切に行わせることができると考えられる。 Here, geometrically, the distance from each vertex to the portions between the vertices of the four adjacent mixing regions 301 is longer than the distance between the sides of each mixing region 301 and the sides of the diffusion region 302, so this distance from each vertex is considered to be the molecular diffusion distance. In this case, the molecular diffusion range of hydrogen, etc. between the sides of each mixing region 301 and the sides of the diffusion region 302 will exceed the planned area, but this will not result in the diffusion of contamination, and it is considered that purification by the diffusion region 302 can be performed sufficiently and appropriately throughout the entire contaminated soil area 203.

また、例えば図5に示すように混合領域を円形混合領域501として形成する場合には、各円形混合領域501の面積は混合領域301よりも大きいが、例えば隣り合う円形混合領域501の中心を結ぶ線上の部分などで円形拡散領域502の重なり代が大きくなりがちであるうえ、汚染土壌エリア203から外方にはみ出す円形混合領域501の領域も大きくなるため、ボーリング孔503の数(ボーリングの回数)も多くなり、浄化剤の使用量も多くなりがちである。 For example, when the mixing area is formed as a circular mixing area 501 as shown in FIG. 5, the area of each circular mixing area 501 is larger than the mixing area 301, but the overlap of the circular diffusion area 502 tends to be large, for example, in the part on the line connecting the centers of adjacent circular mixing areas 501, and the area of the circular mixing area 501 that extends outside the contaminated soil area 203 also becomes large, so the number of boreholes 503 (number of times drilling) tends to increase, and the amount of purification agent used tends to increase.

これに対して、上記のように混合領域301が正方形状など直線状(非円弧状)の境界で区画されるように形成されることにより、汚染土壌エリア203内のボーリングなどの回数を少なく抑えることが容易にでき、浄化の効率も高めることが容易にできる。しかも、汚染土壌エリア203に隣接するエリアが汚染土壌エリアでない場合には、そのような隣接エリアに対して不用意に土壌の切削や浄化剤の混合が行われるのを抑制することもできる。 In contrast, by forming the mixing area 301 as described above so that it is divided by a straight (non-arc) boundary such as a square, it is easy to reduce the number of times drilling and other operations are performed within the contaminated soil area 203, and it is also easy to increase the efficiency of purification. Furthermore, if an area adjacent to the contaminated soil area 203 is not a contaminated soil area, it is also possible to prevent the soil from being cut or the purification agent from being mixed in such an adjacent area inadvertently.

(その他の事項)
上記のような混合領域の形成が行われる場合、その領域の範囲の精度を高くするためには、予め浄化対象の土壌を用いて生分解反応や脱塩素化反応の活性化程度などを計測して、所定時間内におけるボーリング孔の中心から拡散領域の境界までの距離などを推定し、推定された距離に基づいて、ボーリング孔の配置ピッチなどを決定するようにしてもよい。
(Other matters)
When a mixed area as described above is formed, in order to increase the accuracy of the extent of the area, the degree of activation of biodegradation and dechlorination reactions can be measured in advance using the soil to be purified, and the distance from the center of the borehole to the boundary of the diffusion area within a specified time can be estimated, and the arrangement pitch of the boreholes can be determined based on the estimated distance.

また、上記のような推定に代えて、または推定とともに、混合領域の範囲をモニタしながら混合領域の形成をするようにしてもよい。具体的には、例えば図4に示すように、目標とする拡散領域302や混合領域301の外縁部、より詳しくは各領域の頂点部分や辺部分に、計測管と振動センサやマイクロフォンなどから構成される拡散領域外縁検出部401や混合領域外縁検出部402を設け、混合領域が混合領域外縁検出部402の位置まで達し、かつ、拡散領域外縁検出部401の位置までは達しないことを確認するようにしてもよい。また、そのような検出結果をフィードバックして自動的に拡散領域の形成が制御されるようにしてもよい。 In addition, instead of the above estimation, or in addition to the estimation, the mixed region may be formed while monitoring the range of the mixed region. Specifically, for example, as shown in FIG. 4, a diffusion region outer edge detection unit 401 and a mixed region outer edge detection unit 402 consisting of a measurement tube, a vibration sensor, a microphone, etc. may be provided at the outer edge of the target diffusion region 302 or mixed region 301, more specifically, at the vertices and sides of each region, and it may be confirmed that the mixed region reaches the position of the mixture region outer edge detection unit 402 but does not reach the position of the diffusion region outer edge detection unit 401. Furthermore, such detection results may be fed back to automatically control the formation of the diffusion region.

上記のように、水素などの気体が分子拡散した拡散領域が形成されて土壌の浄化が行われる浄化処理において、複数の拡散領域が非円弧状の境界を有し、互いに接し、または重なり合って隣り合うように、特に各混合領域が正方形状や矩形状になるように混合領域や拡散領域の形成が行われることにより、拡散領域が非円弧状の境界を介して隣り合うようになり、拡散領域の境界が円弧状となる場合よりも拡散領域の重なり代を小さく抑え、ボーリングの回数を低減したり領域形成工程の効率を向上させたりすることが容易にできる。また、汚染土壌エリア203の外側に混合領域301が広がる(浄化対象領域を越える)のを防止するとともに、拡散領域302は、汚染土壌エリア203の範囲内では十分に形成されるように(土壌の浄化対象領域以上に形成されるように)することが容易にできる。 As described above, in the purification process in which the diffusion regions are formed by molecular diffusion of gases such as hydrogen and the like to purify the soil, the mixing and diffusion regions are formed so that the multiple diffusion regions have non-arc boundaries and are adjacent to each other or overlap each other, particularly so that each mixing region is square or rectangular. This allows the diffusion regions to be adjacent to each other via non-arc boundaries, and the overlapping of the diffusion regions is smaller than when the boundaries of the diffusion regions are arc-shaped, making it easy to reduce the number of drillings and improve the efficiency of the region formation process. In addition, it is easy to prevent the mixing region 301 from spreading outside the contaminated soil area 203 (beyond the area to be purified), and to ensure that the diffusion region 302 is sufficiently formed within the contaminated soil area 203 (formed beyond the area to be purified).

なお、上記のような拡散領域が形成される浄化方法としては、微生物を利用して水素を発生するものに限らず、浄化剤そのものやその成分、反応生成物などの気体や液体などの物質が分子拡散する場合でも、同様の効果を得ることができる。 The purification method in which the above-mentioned diffusion region is formed is not limited to the method of generating hydrogen using microorganisms, but the same effect can be obtained even when the purification agent itself, its components, reaction products, and other substances such as gases and liquids undergo molecular diffusion.

101 ボーリングロッド
102 噴射装置
102a ノズル
201 浄化対象敷地境界
202 10m区画ライン
203 汚染土壌エリア
301 混合領域
302 拡散領域
303 ボーリング孔
401 拡散領域外縁検出部
402 混合領域外縁検出部
501 円形混合領域
502 円形拡散領域
503 ボーリング孔
REFERENCE SIGNS LIST 101 Boring rod 102 Injection device 102a Nozzle 201 Boundary of site to be purified 202 10m division line 203 Contaminated soil area 301 Mixing area 302 Diffusion area 303 Borehole 401 Diffusion area outer edge detection unit 402 Mixing area outer edge detection unit 501 Circular mixing area 502 Circular diffusion area 503 Borehole

Claims (6)

汚染された土壌を浄化する汚染土壌浄化方法であって、
ボーリング孔を形成するボーリング孔形成工程と、
上記ボーリング孔に噴射装置を挿入して回転させながら水を高圧で噴射して土壌の面状でスリット状の領域を切削し、浄化剤を圧入・充填することにより、土壌と浄化剤とが混合された混合領域、および上記混合領域の上記面状でスリット状の領域に沿った方向の周囲に所定の物質が分子拡散する拡散領域を形成する領域形成工程と、
を有し、
上記領域形成工程は、形成される複数の拡散領域が非円弧状の境界を有し、互いに接し、または重なり合って隣り合うように行われるとともに、形成される複数の混合領域は互いに接さず重なり合うこともないように行われることを特徴とする汚染土壌浄化方法。
A method for remediating contaminated soil, comprising:
a borehole forming step of forming a borehole;
a region forming process in which an injection device is inserted into the borehole and rotated while injecting water at high pressure to cut a slit-shaped area on the surface of the soil, and then a purification agent is injected and filled into the borehole to form a mixed region in which the soil and purification agent are mixed, and a diffusion region in which a predetermined substance diffuses molecularly around the mixed region in a direction along the planar slit-shaped area ;
having
The above-mentioned region formation process is carried out so that the multiple diffusion regions formed have non-arc-shaped boundaries and are adjacent to each other and adjacent to each other, either in contact or overlapping relation, and the multiple mixed regions formed are carried out so that they are neither in contact with each other nor overlapping each other, in accordance with a contaminated soil purification method.
請求項1の汚染土壌浄化方法であって、
上記混合領域は、矩形状の領域であることを特徴とする汚染土壌浄化方法。
The method for remediating contaminated soil according to claim 1,
A method for remediating contaminated soil, wherein the mixing area is a rectangular area.
請求項1から請求項2のうち何れか1項の汚染土壌浄化方法であって、
上記浄化剤は、地中に存在する微生物の生分解反応により水素を発生させる微生物活性剤であり、上記拡散領域は、発生した水素が分子拡散する領域であることを特徴とする汚染土壌浄化方法。
The method for remediating contaminated soil according to any one of claims 1 to 2,
A method for purifying contaminated soil, characterized in that the purification agent is a microbial activator that generates hydrogen through a biodegradation reaction of microorganisms present in the ground, and the diffusion area is an area where the generated hydrogen diffuses molecularly.
請求項3の汚染土壌浄化方法であって、
上記ボーリング孔の中心から上記拡散領域の境界までの距離が、予め浄化対象の土壌を用いた上記生分解反応の活性化程度の計測に基づいて推定され、推定された距離に基づいて、ボーリング孔の配置ピッチが決定されることを特徴とする汚染土壌浄化方法。
The method for remediating contaminated soil according to claim 3,
A method for remediating contaminated soil, characterized in that the distance from the center of the borehole to the boundary of the diffusion zone is estimated based on a measurement of the degree of activation of the biodegradation reaction using the soil to be remediated in advance, and the arrangement pitch of the boreholes is determined based on the estimated distance.
請求項1から請求項4のうち何れか1項の汚染土壌浄化方法であって、
上記ボーリング孔の中心から所定の距離の位置に、上記浄化剤の到達の有無を検出する検出手段を配置して、上記浄化剤の噴射による土壌の切削を行うことを特徴とする汚染土壌浄化方法。
The method for remediating contaminated soil according to any one of claims 1 to 4,
A method for remediating contaminated soil, characterized in that a detection means for detecting whether or not the purification agent has reached the borehole is located at a predetermined distance from the center of the borehole, and the soil is cut by spraying the purification agent.
請求項1から請求項5のうち何れか1項の汚染土壌浄化方法であって、
上記混合領域は、土壌の浄化対象領域を越えないとともに、上記拡散領域は、土壌の浄化対象領域以上に形成されることを特徴とする汚染土壌浄化方法。
The method for remediating contaminated soil according to any one of claims 1 to 5,
A method for remediating contaminated soil, characterized in that the mixing area does not extend beyond the area of the soil to be remediated, and the diffusion area is formed to be larger than the area of the soil to be remediated.
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