JP2011167619A - Contaminated soil cleaning method - Google Patents

Contaminated soil cleaning method Download PDF

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JP2011167619A
JP2011167619A JP2010032851A JP2010032851A JP2011167619A JP 2011167619 A JP2011167619 A JP 2011167619A JP 2010032851 A JP2010032851 A JP 2010032851A JP 2010032851 A JP2010032851 A JP 2010032851A JP 2011167619 A JP2011167619 A JP 2011167619A
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contaminated soil
underground
soil
mixed material
underground pile
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JP5721331B2 (en
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Norio Watanabe
則雄 渡辺
Nobuyuki Kadokura
伸行 門倉
Tatsuya Ito
達也 伊藤
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Kumagai Gumi Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a contaminated soil cleaning method for cleaning contaminated soil, at the same time, performing ground strengthening and, even after the ground strengthening, cleaning contaminated soil and contaminated ground water. <P>SOLUTION: The contaminated soil cleaning method is a method of cleaning soil by vertically disposing an underground pile 54a to the contaminated soil 50, and includes: a process of digging a pit 51 up to a depth where contaminated earth 52 exists; and a process of charging, in the pit 51, mixed material C for underground pile formation made by mixing discharge earth discharged by digging or earth B for underground formation prepared beforehand and an alkali activation persulfate as a cleaning agent A selected from among any of sodium persulfate, potassium persulfate and ammonium persulfate into the pit, and burying the pit 51 back, and after charging the mixed material C for underground pile formation into the pit 51, sodium hydroxide or potassium hydroxide is charged into the pit 51, and thus the cleaning is performed. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

本発明は、地盤中の汚染土壌の浄化と地盤強化を同時に行うことが可能な汚染土壌浄化方法に関する。   The present invention relates to a contaminated soil purification method capable of simultaneously purifying contaminated soil in the ground and strengthening the ground.

従来、汚染土壌の浄化方法としては、特許文献1に示すように、水溶液状の過酸化物、例えば、フェントン試薬、過マンガン酸カリウムを汚染土壌に混入して酸化反応させ、汚染物質として有機塩素化合物からなる油(石油系炭化水素,多環芳香族炭化水素等),ベンゼン,トルエン,キシレン,塩素化エチレン(トリクロロエチレン,テトラクロロエチレン,ジクロロエチレン等)を無機化することが知られている。
具体的には、フェントン試薬によるフェントン反応を利用する浄化方法は、過酸化水素水に触媒としての二価の鉄イオンを反応させてヒドロキシラジカルを生成し、上記有機塩素化合物と反応させることで、二酸化炭素、水、塩素イオン及び水素イオンに分解し、無機化して汚染土壌を浄化している。
Conventionally, as a method for purifying contaminated soil, as shown in Patent Document 1, an aqueous peroxide, for example, Fenton reagent and potassium permanganate are mixed in the contaminated soil to cause an oxidation reaction, and organic chlorine is used as the contaminant. It is known to mineralize compound oils (petroleum hydrocarbons, polycyclic aromatic hydrocarbons, etc.), benzene, toluene, xylene, chlorinated ethylenes (trichloroethylene, tetrachloroethylene, dichloroethylene, etc.).
Specifically, the purification method utilizing the Fenton reaction by the Fenton reagent generates a hydroxyl radical by reacting a hydrogen peroxide solution with a divalent iron ion as a catalyst, and reacts with the organochlorine compound. It decomposes into carbon dioxide, water, chlorine ions and hydrogen ions, mineralizes it and purifies contaminated soil.

上記反応を用いた浄化方法は、特許文献2や特許文献3に示すように、例えば、アースドリルやオーガマシンにより汚染土の存在する地層まで竪孔を掘削し、この竪孔に直接、浄化剤としての水溶液状の過酸化物を投入することで、汚染物質と反応させて無機化して竪孔周囲の地層を浄化した後に、掘削の際に排出された浄化済の土で埋め戻すことにより行われる。
また、汚染土壌は、地層中に含まれる水分が移動することで汚染物質が広範囲に拡散し、特に、近傍に地下水が流れるような水分を多く含んだ軟弱な地盤に多く見られることが知られ、このような土壌を利用,再利用する場合には、土壌汚染の浄化と合わせて土壌改良を行う必要があり、一般には、汚染土壌の浄化を行った後の地層中に地中杭が造成される。
As shown in Patent Document 2 and Patent Document 3, for example, a purification method using the above reaction is to excavate a fistula to a formation where contaminated soil exists by using an earth drill or an auger machine, As an aqueous solution of peroxide, it is made mineral by reacting with pollutants and purifying the formation around the fistula, and then backfilling with the purified soil discharged during excavation. Is called.
In addition, it is known that contaminated soil is widely seen in soft ground that contains a lot of moisture, such as groundwater flowing nearby, due to the diffusion of contaminants in a wide range due to the movement of moisture contained in the formation. When using or reusing such soil, it is necessary to improve the soil in conjunction with the purification of soil contamination. Generally, underground piles are created in the stratum after purification of the contaminated soil. Is done.

しかしながら、竪孔内に直接、浄化剤である水溶液状の過酸化物質を投入又は注入する場合、汚染物質と過酸化物質が投入直後から局所的に急激に反応が進むため、反応した物質が噴出する危険性がある。また、浄化処理を行う地層は多くの水分を含み、近傍に地下水が流れていることが多いため、浄化剤が局所的な反応をするか、十分に汚染物質と反応することなく地下水に流されてしまうため、汚染土壌の浄化を効率的に行うことができないという問題がある。
また、汚染土を汚染土が存在する地層から取り除き、処理施設に搬送して浄化した後に再び埋め戻す方法や浄化処理済の土により埋め戻す方法もあるが、汚染土を掘削して搬送し、浄化処理済の土を再び搬送して埋め戻す必要があるため、汚染土壌の浄化にかかる手間と費用が膨大になるとともに長い工期が必要となってしまい経済的に非効率的である。
However, when an aqueous peroxide as a cleaning agent is directly injected or injected into the fistula, the reaction rapidly proceeds locally immediately after the pollutant and peroxide are introduced, and the reacted substance is ejected. There is a risk of doing. In addition, since the stratum that performs the purification treatment contains a lot of water and the groundwater often flows in the vicinity, the purification agent reacts locally or does not sufficiently react with pollutants and is washed away into the groundwater. Therefore, there is a problem that the contaminated soil cannot be purified efficiently.
In addition, there is a method of removing contaminated soil from the strata where the contaminated soil exists, transporting it to a treatment facility and purifying it, and then backfilling it again with soil that has been purified, or excavating and transporting the contaminated soil, Since it is necessary to transport and backfill the soil that has been subjected to the purification treatment, the labor and cost for the purification of the contaminated soil become enormous and a long construction period is required, which is economically inefficient.

特開2004−183310号公報JP 2004-183310 A 特開2002−188137号公報JP 2002-188137 A 特開2009−56356号公報JP 2009-56356 A

本発明は、前記課題を解決するため、汚染土壌を浄化すると同時に地盤強化を行い、かつ、地盤強化後においても汚染土壌及び汚染された地下水の浄化を可能とする汚染土壌浄化方法を提供する。   In order to solve the above-described problems, the present invention provides a method for purifying contaminated soil that purifies contaminated soil and simultaneously strengthens the ground, and enables purification of contaminated soil and contaminated groundwater even after the ground is strengthened.

本発明に係る第1の形態として、汚染土壌に地中杭を立設して土壌を浄化する方法であって、汚染土が存在する深さまで竪孔を掘削する工程と、掘削により排出された排出土又はあらかじめ用意された地中杭造成用土と過硫酸ナトリウム、過硫酸カリウム、過硫酸アンモニウムのうちいずれかから選択されるアルカリ活性化過硫酸塩とが混合された地中杭造成用混合材を竪孔内に投入して竪孔を埋め戻す工程とを含み、地中杭造成用混合材を竪孔内に投入した後に、水酸化ナトリウム又は水酸化カリウムを竪孔内に投入する形態とした。
本発明によれば、排出土または地中杭造成用土に汚染土の浄化剤としてのアルカリ活性化過硫酸塩を混合して、掘削した竪孔に埋め戻して地中杭を立設することにより、造成した地中杭から土壌を浄化する浄化物質が染み出して、地中杭の周囲に存在する汚染土を浄化することが可能となる。さらに、この地中杭を通過する地下水に含まれる汚染物質が浄化されるので、地中杭設置後においても長期間に渡って汚染物質を浄化することができる。
また、浄化剤を過硫酸ナトリウム、過硫酸カリウム、過硫酸アンモニウムのうちいずれかから選択されるアルカリ活性化過硫酸塩とすれば、アルカリ活性化過硫酸塩が常態において、固体であることから排出土や地中造成用土と混合することで急激に反応することがなく、混合作業が安全になり、汚染土壌を浄化する施設だけでなく、地中杭を造成する現場で混合作業をすることができる。
また、地中杭造成用混合材に含まれるアルカリ活性化過硫酸塩と汚染物質とを反応させる触媒としての水酸化ナトリウム又は水酸化カリウムを投入することで、汚染物質との反応を連鎖的に行わせることが可能となり、効率的に浄化することができる。
本発明に係る第2の形態として、竪孔を埋め戻す工程は、竪孔内に貫入されたケーシング内に地中杭造成用混合材を投入し、地中杭造成用混合材をケーシング内部のスラストスクリューの回転力で地中杭造成用混合材を竪孔内で締め固める形態とした。
本発明によれば、地中杭造成用混合材がスラストスクリューの回転力により竪孔内で締め固められることで、地中杭を形成する地中杭造成用混合材が圧縮され、強固な地中杭を造成することが可能となる。
本発明に係る第3の形態として、アルカリ活性化過硫酸塩は、水溶性高分子により被覆されるようにした。
本発明によれば、アルカリ活性化過硫酸塩が水溶性高分子により被覆されることにより、直ちにアルカリ活性化過硫酸塩が地中の水分と反応することがないので、水溶性高分子の被覆からアルカリ活性化過硫酸塩を徐々に滲出させて、アルカリ活性化過硫酸塩を汚染土壌の広範囲に浸透させることができる。
本発明に係る第4の形態として、水酸化ナトリウム又は水酸化カリウムの投入と地中杭造成用混合剤の締め固めとを交互に行い、当該締め固められた地中杭造成用混合材を竪孔内における汚染土が存在する高さまで到達させるようにした。
本発明によれば、水酸化ナトリウム又は水酸化カリウムの投入と地中杭造成用混合材の締め固めとを交互に行うことにより、締め固められる地中杭造成用混合材に対して均一に水酸化ナトリウム又は水酸化カリウムを行き渡らせることが可能となる。
本発明に係る第5の形態として、水酸化ナトリウム又は水酸化カリウムは、締め固められた地中杭造成用混合材を竪孔内における汚染土が存在する高さまで到達させた後に投入するようにした。
本発明によれば、水溶性高分子の被覆からアルカリ活性化過硫酸塩を徐々に滲出させて、アルカリ活性化過硫酸塩を汚染土壌の広範囲に浸透させた後に、水酸化ナトリウム又は水酸化カリウムが投入されるので、広範囲の汚染土壌を浄化することができる。
本発明に係る第6の形態として、締め固めにより、竪孔における汚染土が存在する高さの範囲を拡径するようにした。
本発明によれば、竪孔における汚染土が存在する高さの範囲を拡径することにより、汚染土が存在する地層における単位面積あたりの地中杭が存在する割合を高めることができるので、より広範囲な浄化が可能となる。
本発明に係る第7の形態として、汚染土壌に複数の地中杭を立設する場合において、竪孔の孔径は汚染土壌を平面視したときに拡径後の竪孔同士がラップする孔径とするようにした。
本発明によれば、汚染土壌に立設された複数の地中杭が汚染土が存在する範囲において重なり合うため、汚染土が存在する地層における単位面積あたりの地中杭が存在する割合をより高めることができるので、より広範囲な浄化が可能となる。
As a first embodiment according to the present invention, a method for purifying soil by erecting underground piles in contaminated soil, a step of excavating a fistula to a depth where contaminated soil exists, and discharged by excavation An underground pile building mixed material in which discharged soil or previously prepared underground pile building soil and alkali-activated persulfate selected from sodium persulfate, potassium persulfate, and ammonium persulfate are mixed And a step of filling the borehole and filling the borehole, and after charging the underground pile building material into the borehole, sodium hydroxide or potassium hydroxide is put into the borehole. .
According to the present invention, by mixing alkali-activated persulfate as a purification agent for contaminated soil into the soil for discharging soil or underground pile construction, it is backfilled in the excavated borehole, and the underground pile is erected. The purification substance that purifies the soil exudes from the created underground pile, and it becomes possible to purify the contaminated soil existing around the underground pile. Furthermore, since the pollutant contained in the groundwater passing through the underground pile is purified, the contaminant can be purified over a long period of time even after the underground pile is installed.
In addition, if the cleaning agent is an alkali activated persulfate selected from sodium persulfate, potassium persulfate, and ammonium persulfate, the alkaline activated persulfate is normally solid and discharged. And mixing with the soil for underground construction, the mixing work becomes safe, and the mixing work can be done not only at the facility to purify the contaminated soil, but also at the site where the underground pile is created .
In addition, by introducing sodium hydroxide or potassium hydroxide as a catalyst for reacting alkali-activated persulfate and pollutants contained in the underground pile building mixture, reaction with pollutants can be chained. It becomes possible to carry out, and it can purify | clean efficiently.
As a second form according to the present invention, the step of refilling the fistula is to insert the underground pile forming mixed material into the casing penetrating into the fistula, and to add the underground pile forming mixed material to the inside of the casing. It was made into the form which the mixture material for underground pile construction was compacted in the fistula by the rotational force of a thrust screw.
According to the present invention, the underground pile forming mixed material is compacted in the borehole by the rotational force of the thrust screw, so that the underground pile forming mixed material forming the underground pile is compressed, and the strong underground It becomes possible to create a medium pile.
As a third aspect of the present invention, the alkali-activated persulfate is coated with a water-soluble polymer.
According to the present invention, the alkali-activated persulfate is coated with the water-soluble polymer, so that the alkali-activated persulfate does not immediately react with moisture in the ground. The alkali-activated persulfate can be gradually leached from the soil to allow the alkali-activated persulfate to permeate a wide range of contaminated soil.
As a fourth embodiment according to the present invention, sodium hydroxide or potassium hydroxide is charged and compaction of the underground pile forming mixture is alternately performed. It was made to reach the height where the contaminated soil exists in the hole.
According to the present invention, by introducing sodium hydroxide or potassium hydroxide and compacting the underground pile forming mixed material alternately, water is uniformly distributed to the ground pile forming mixed material to be compacted. It becomes possible to spread sodium oxide or potassium hydroxide.
As 5th form which concerns on this invention, sodium hydroxide or potassium hydroxide is thrown in after making the compacted underground pile formation mixed material reach the height where the contaminated soil exists in the borehole. did.
According to the present invention, the alkali-activated persulfate is gradually leached from the coating of the water-soluble polymer, and the alkali-activated persulfate is infiltrated into a wide area of the contaminated soil, and then sodium hydroxide or potassium hydroxide. Can be used to purify a wide range of contaminated soil.
As a sixth embodiment according to the present invention, the range of the height where the contaminated soil exists in the fistula is expanded by compaction.
According to the present invention, it is possible to increase the ratio of underground piles per unit area in the formation where the contaminated soil exists by expanding the range of the height where the contaminated soil exists in the fistula, A wider range of purification is possible.
As a seventh embodiment according to the present invention, in the case where a plurality of underground piles are erected in the contaminated soil, the hole diameter of the fistula is a hole diameter that the fistulas after diameter expansion wraps when the contaminated soil is viewed in plan view. I tried to do it.
According to the present invention, since a plurality of underground piles erected on the contaminated soil overlap in a range where the contaminated soil exists, the proportion of underground piles per unit area in the stratum where the contaminated soil exists is further increased. A wider range of purification is possible.

本発明に係る汚染土壌浄化方法に用いられる汚染土壌改良装置を示す概略図。Schematic which shows the contaminated soil improvement apparatus used for the contaminated soil purification method which concerns on this invention. 本発明に係る汚染土壌浄化方法の工程図。The process drawing of the contaminated soil purification method which concerns on this invention. 本発明に係る汚染土壌浄化方法の工程図。The process drawing of the contaminated soil purification method which concerns on this invention. 本発明に係る地中杭造成位置を示す平面図。The top view which shows the underground pile creation position which concerns on this invention. 本発明に係る他の形態の汚染土壌浄化方法の工程図。The process figure of the contaminated soil purification method of the other form which concerns on this invention. 本発明に係る他の形態の地中杭造成位置を示す平面図。The top view which shows the underground pile creation position of the other form which concerns on this invention.

以下、発明の実施形態を通じて本発明を詳説するが、以下の実施形態は特許請求の範囲に係る発明を限定するものではなく、また実施形態の中で説明される特徴の組み合わせの全てが発明の解決手段に必須であるとは限らず、選択的に採用される構成を含むものである。   Hereinafter, the present invention will be described in detail through embodiments of the invention. However, the following embodiments do not limit the invention according to the claims, and all combinations of features described in the embodiments are included in the invention. It is not necessarily essential to the solution, but includes a configuration that is selectively adopted.

実施形態1
以下、本発明の汚染土壌の浄化方法について、図面を参照して詳細に説明する。
図1は、汚染土壌50を浄化する汚染土壌改良装置を示し、同図において、汚染土壌改良装置は地盤改良等に用いられるクレーン1を備える。クレーン1は、任意の作業位置に移動可能なクローラ2と、このクローラ2の上に搭載される水平方向に旋回自在な台車3と、台車3前部に垂直上方に立設されるポスト4と、台車3後部から延長され、ポスト上部4aと接続してポスト4を支持するバックステー5と、ワイヤ7を巻取り、巻出しするウインチ6とを備える。ワイヤ7は、ウインチ6及びポスト上端部4bに設けられたシーブ部8のプーリに掛け渡されて、ワイヤ先端7aに汚染土壌50を掘削するためのケーシング用オーガマシン11やスラストスクリュー用オーガマシン12が吊設される。
Embodiment 1
Hereinafter, the purification method for contaminated soil of the present invention will be described in detail with reference to the drawings.
FIG. 1 shows a contaminated soil improvement device for purifying contaminated soil 50. In the figure, the contaminated soil improvement device includes a crane 1 used for ground improvement or the like. The crane 1 includes a crawler 2 that can be moved to an arbitrary work position, a horizontally-movable cart 3 that is mounted on the crawler 2, and a post 4 that is erected vertically above the front of the cart 3. The back stay 5 extends from the rear portion of the carriage 3 and is connected to the post upper portion 4a to support the post 4, and the winch 6 that winds and unwinds the wire 7. The wire 7 is hung on a pulley of a sheave portion 8 provided on the winch 6 and the post upper end portion 4b, and a casing auger machine 11 and a thrust screw auger machine 12 for excavating the contaminated soil 50 on the wire tip 7a. Is suspended.

ケーシング用オーガマシン11は、図1に示すように、中空状のケーシング14と、ケーシング14を回転させる図外のモータと、後述の地中杭造成用混合材Cを投入するホッパ15とを備え、ケーシング14はワイヤ7で吊設されることにより汚染土壌50の地表面に対して略垂直に設置される。
スラストスクリュー用オーガマシン12は、ケーシング用オーガマシン11の上部に設けられ、ケーシング14の延長方向内部に貫通するシャフト16と、シャフト16を回転駆動する図外のモータとを備える。シャフト16は内部にシャフト16の延長方向に渡って貫通する貫通孔18を有し、当該貫通孔18の上端部は流体供給手段20と接続される。流体供給手段20は、後述の触媒Dとしての水酸化ナトリウム又は水酸化カリウムを貫通孔18の先端部18aから吐出させる装置である。また、シャフト16は、汚染土壌50側の外周面にスラストスクリュー17を備え、スラストスクリュー17の先端17aとケーシング14の先端とがほぼ面一となるようにケーシング14の中心に配置される。
汚染土壌50に対して竪孔51を掘削する際には、各オーガマシン11,12の自重で汚染土壌50の地表面に荷重をかけつつ、図外モータの駆動によりケーシング14を回転させながら貫入し、ケーシング14の外側表面から地上に土を排出しつつ、汚染土壌50における汚染土52を含む地層まで竪孔51を形成する。以下、具体的に説明する。
As shown in FIG. 1, the casing auger machine 11 includes a hollow casing 14, a motor (not shown) that rotates the casing 14, and a hopper 15 that feeds the underground pile building mixture C described later. The casing 14 is installed substantially perpendicular to the ground surface of the contaminated soil 50 by being suspended by the wire 7.
The auger machine 12 for thrust screw is provided in the upper part of the auger machine 11 for casings, and includes a shaft 16 that penetrates the casing 14 in the extending direction and a motor (not shown) that rotationally drives the shaft 16. The shaft 16 has a through hole 18 penetrating in the extending direction of the shaft 16 inside, and an upper end portion of the through hole 18 is connected to the fluid supply means 20. The fluid supply means 20 is a device that discharges sodium hydroxide or potassium hydroxide as a catalyst D described later from the tip end portion 18 a of the through hole 18. The shaft 16 includes a thrust screw 17 on the outer peripheral surface on the contaminated soil 50 side, and is disposed at the center of the casing 14 so that the tip 17a of the thrust screw 17 and the tip of the casing 14 are substantially flush with each other.
When excavating the borehole 51 in the contaminated soil 50, the load is applied to the ground surface of the contaminated soil 50 by the weight of each auger machine 11 and 12, and the casing 14 is rotated by driving the motor outside the figure. Then, while discharging the soil from the outer surface of the casing 14 to the ground, the fistula 51 is formed up to the formation including the contaminated soil 52 in the contaminated soil 50. This will be specifically described below.

まず、図2(a),(b)に示すように、汚染土壌50における汚染土52が存在する地層に到達するまでケーシング14を回転させつつ貫入することで竪孔51を形成する。具体的には、竪孔51の底部51aが汚染土52が存在する地層の最深部にまで到達するまでケーシング14を貫入する。また、竪孔51を形成するに際して排出される汚染土52を含む土は、例えばダンプトラック等により、図外の土壌の浄化処理施設に搬送され後述の地中杭造成用混合材Cを構成する地中杭として用いられる。   First, as shown in FIGS. 2A and 2B, the fistula 51 is formed by penetrating the casing 14 while rotating the casing 14 until reaching the formation where the contaminated soil 52 exists in the contaminated soil 50. Specifically, the casing 14 is penetrated until the bottom 51a of the hole 51 reaches the deepest part of the formation where the contaminated soil 52 exists. Further, the soil including the contaminated soil 52 discharged when forming the fistula 51 is conveyed to a soil purification treatment facility (not shown) by, for example, a dump truck, and constitutes an underground pile building mixed material C described later. Used as underground pile.

次に、図2(c)に示すように所定の深さまで竪孔51を形成した後に、竪孔51内にホッパ15を介してケーシング14の下方に地中杭造成用混合材Cを投入する。地中杭造成用混合材Cは、浄化剤Aと地中造成用土Bとが混合されることにより構成されるものであって、浄化剤Aとしては過硫酸ナトリウム、過硫酸カリウム、過硫酸アンモニウム等のアルカリ活性化過硫酸塩が好ましく、地中造成用土Bとしては、竪孔51を形成する際に排出された排出土又は当該排出土とは別にあらかじめ用意された浄化済の砂や砕石が混ぜられた地中杭造成用の土が採用される。
浄化剤Aをアルカリ活性化過硫酸塩としたのは、アルカリ活性化過硫酸塩が通常の状態として固体、例えば粉体であるため、地中造成用土Bとの混合作業がし易く、かつ、竪孔51内に埋め戻されたときに汚染土壌50に存在する水分と反応することで液化し、液化したアルカリ活性化過硫酸塩と汚染物質とが穏やかに反応することから安全に埋め戻し作業を行うことができるからである。
Next, as shown in FIG. 2 (c), after the dredging hole 51 is formed to a predetermined depth, the underground pile forming mixed material C is put into the dredging hole 51 through the hopper 15 and below the casing 14. . The underground pile creation mixed material C is constituted by mixing the purification agent A and the underground development soil B, and as the purification agent A, sodium persulfate, potassium persulfate, ammonium persulfate, etc. Alkaline-activated persulfate is preferable, and as the soil B for underground construction, the discharged soil discharged when forming the borehole 51 or purified sand or crushed stone prepared separately from the discharged soil is mixed. The soil for building underground piles is adopted.
The purification agent A is an alkali-activated persulfate because the alkali-activated persulfate is a solid, for example, a powder as a normal state, so that it can be easily mixed with the underground soil B, and When it is backfilled in the fistula 51, it reacts with the water present in the contaminated soil 50 and liquefies, and the liquefied alkali-activated persulfate and the pollutant react gently so that it can be safely backfilled. It is because it can be performed.

以下、浄化剤Aとして過硫酸ナトリウムを用いて地中杭造成用混合材Cを作成し、当該地中杭造成用混合材Cを竪孔51における汚染土52が存在する範囲に投入した場合の化学反応について説明する。
(1)水和反応:Na(過硫酸ナトリウム)+HO →S ―+Na
この反応により、粉体であった過硫酸ナトリウムは竪孔51の周囲の地層に含まれる水分と反応して、水溶液となり、水溶液中で硫酸イオンとナトリウムイオンとなる。
(2)この水溶液にアルカリ活性化剤としての水酸化ナトリウム又は水酸化カリウムを汚染物質との反応触媒Dとして注入することで、反応が促進されて次のような反応を示す。
―+Na+ +OH−↓
SO−・(硫酸ラジカル)+HO → HSO −+OH・(ヒドロキシラジカル)
この反応では、ヒドロキシラジカルと汚染物質とが、連鎖的に反応することで汚染物質がRH → R・となる。
なお、RHは汚染物質を示し、例えば、油(石油系炭化水素、多環芳香族炭化水素)、ベンゼン、トルエン、キシレン、塩素化エチレン(トリクロロエチレン、テトラクロロエチレン、ジクロロエチレン他)と反応して無機化され、例えば、HO、CO、ハロゲン物質等になり無害の物質に変換されて土壌が浄化される。
Hereinafter, the underground pile creation mixed material C is prepared using sodium persulfate as the purification agent A, and the underground pile creation mixed material C is put into a range where the contaminated soil 52 in the borehole 51 exists. The chemical reaction will be described.
(1) Hydration reaction: Na 2 S 2 O 8 (sodium persulfate) + H 2 O → S 2 O 8 2 − + Na 2 +
Due to this reaction, the powdered sodium persulfate reacts with moisture contained in the formation around the fistula 51 to form an aqueous solution, which becomes sulfate ions and sodium ions in the aqueous solution.
(2) By injecting sodium hydroxide or potassium hydroxide as an alkali activator into the aqueous solution as a reaction catalyst D with a pollutant, the reaction is promoted to show the following reaction.
S 2 O 8 2 − + Na 2 + + OH− ↓
SO 4 − · (sulfuric acid radical) + H 2 O → HSO 4 2 − + OH · (hydroxy radical)
In this reaction, the hydroxyl radical and the pollutant react in a chain reaction, so that the pollutant becomes RH → R ·.
RH indicates a pollutant and is made mineral by reacting with oil (petroleum hydrocarbon, polycyclic aromatic hydrocarbon), benzene, toluene, xylene, chlorinated ethylene (trichloroethylene, tetrachloroethylene, dichloroethylene, etc.), for example. For example, it becomes H 2 O, CO 2 , a halogen substance, etc. and is converted into a harmless substance, and the soil is purified.

図2(d)に戻り、地中杭造成用混合材Cの埋め戻し工程について説明する。ケーシング14に投入された地中杭造成用混合材Cは、スラストスクリュー17の上端面上に蓄積する。そしてこの状態において、スラストスクリュー17を竪孔51に排出する方向に回転させて、複数のスクリューフィン間に地中杭造成用混合材Cを充填し、さらにスラストスクリュー17を回転させることにより竪孔51の底部51aに向けて地中杭造成用混合材Cを排出する。また、スラストスクリュー17の回転開始と同時にケーシング14をスラストスクリュー17の回転方向とは逆方向に回転させて、スラストスクリュー17とケーシング14の先端を徐々に地表側に移動させることにより、竪孔51の底部51aとケーシング14の先端までの空間に地中杭造成用混合材Cを充填する。地中杭造成用混合材Cの埋め戻し後、シャフト16の先端部18aから貫通孔18を介して供給される触媒Dを埋め戻された地中杭造成用混合材Cに対して注入する。なお、地中杭造成用混合材Cの排出と、触媒Dの注入とを同時に行ってもよい。即ち、地中杭造成用混合材Cの排出開始と同時に触媒Dの注入を開始し、排出される地中杭造成用混合材Cに触媒Dを含ませるようにすれば、地中杭造成用混合材Cに対して触媒Dを一層均一に浸透させることができる。   Returning to FIG. 2D, the backfilling process of the underground pile building mixed material C will be described. The underground pile forming mixed material C charged into the casing 14 accumulates on the upper end surface of the thrust screw 17. In this state, the thrust screw 17 is rotated in the direction to be discharged into the hole 51, the underground pile forming mixed material C is filled between the plurality of screw fins, and the thrust screw 17 is further rotated to make the hole. The underground pile building mixed material C is discharged toward the bottom 51a of 51. Further, simultaneously with the start of rotation of the thrust screw 17, the casing 14 is rotated in the direction opposite to the rotation direction of the thrust screw 17, and the thrust screw 17 and the tip of the casing 14 are gradually moved to the ground surface side, so that the bore 51 The space between the bottom 51a and the tip of the casing 14 is filled with the underground pile forming mixed material C. After backfilling the underground pile building material C, the catalyst D supplied from the tip 18a of the shaft 16 through the through hole 18 is injected into the backfilled underground pile building material C. In addition, you may perform discharge | emission of the mixing material C for underground pile construction, and injection | pouring of the catalyst D simultaneously. That is, if the injection of the catalyst D is started simultaneously with the start of the discharge of the underground pile building mixed material C, and the catalyst D is included in the discharged underground pile building mixed material C, the underground pile building use The catalyst D can be more uniformly permeated into the mixed material C.

図2(e)に示すように、上記地中杭造成用混合材Cの埋め戻し工程終了後には、地中杭造成用混合材Cの締め固め工程が実行される。具体的には、ケーシング14の回転を停止した後に、スラストスクリュー17のみに回転力を与え、地中杭造成用混合材Cを竪孔51の底部51aに向けて排出し、竪孔51の底部51aに充填された地中杭造成用混合材Cの締め固めを行う。そして、さらに地中杭造成用混合材Cを投入し、スラストスクリュー17を回転させることにより、竪孔51の当初の孔径D1を孔径D2に拡径させることができる。当該締め固め工程により、地中杭造成用混合材Cに注入された触媒Dが下方に向かって浸透するので地中杭造成用混合材Cに対して触媒Dを均一に拡散することができる。
なお、上記埋め戻し及び締め固めによる拡径の作業において、スラストスクリュー17に作用する抵抗を図外のモータの駆動トルクの変化として検出すれば、トルクの変化を測定することで締め固めにより拡径した孔径がわかるので、孔径D1から孔径D2に拡径されるまでのトルクの変化を例えば、図外のスラストスクリュー用オーガマシン12のモータの制御装置に記憶しておくことで容易に拡径作業を行うことができる。
As shown in FIG.2 (e), after completion | finish of the backfilling process of the said underground pile formation mixed material C, the compacting process of the underground pile formation mixed material C is performed. Specifically, after the rotation of the casing 14 is stopped, a rotational force is applied only to the thrust screw 17, the underground pile building mixed material C is discharged toward the bottom 51 a of the bore 51, and the bottom of the bore 51 The underground pile building mixed material C filled in 51a is compacted. Further, by introducing the underground pile forming mixed material C and rotating the thrust screw 17, the initial hole diameter D1 of the bore 51 can be expanded to the hole diameter D2. By the compaction step, the catalyst D injected into the underground pile building mixture C permeates downward, so that the catalyst D can be uniformly diffused into the underground pile building mixture C.
If the resistance acting on the thrust screw 17 is detected as a change in the driving torque of the motor (not shown) in the above-described work of expanding the diameter by backfilling and compacting, the diameter is expanded by compaction by measuring the torque change. Since the change in torque until the hole diameter is increased from the hole diameter D1 to the hole diameter D2 is stored in, for example, the motor control device of the auger machine 12 for thrust screw (not shown), the diameter expansion work can be easily performed. It can be performed.

以上の埋め戻し工程、及び、締め固め工程により、竪孔51における汚染土52が存在する高さの範囲の一部に形成される地中杭の一回の作成工程が終了し、当該工程を繰り返すことにより、地中杭造成用混合材Cからなる地中杭を汚染土52が存在する高さT1まで到達するように造成する。即ち、図3(f)乃至(j)に示すように、一回の作成工程により造成された地中杭54aの上方の竪孔51を再度埋め戻し、締め固めることにより二段目の地中杭54bを作成し、さらに二段目の地中杭54bの上方の竪孔51を埋め戻し、締め固めることにより三段目の地中杭54cを作成することより、少なくとも汚染土52が存在する高さの範囲に渡って拡径された地中杭54を造成することができる。
即ち、地中杭54は、汚染土52が存在する地中側の境界52aまでを掘削して形成された竪孔51に地中杭造成用混合材Cを投入して埋め戻し、この埋め戻された地中杭造成用混合材Cに対して触媒Dを注入して締め固めるとともに拡径して一段目の地中杭54aを造成し、地中杭54aの上に地中杭造成用混合材Cを投入して埋め戻し、埋め戻された地中杭造成用混合材Cに対して触媒Dを注入して締め固めるとともに竪孔51を拡径して二段目の地中杭54bを造成し、地中杭54bの上に地中杭造成用混合材Cを投入して埋め戻し、埋め戻された地中杭造成用混合材Cに対して触媒Dを注入して締め固めるとともに竪孔51を拡径して三段目の地中杭54cを造成し、このように、触媒Dの注入と地中杭造成用混合材Cの締め固めを交互に汚染土52が存在する地表側の境界52bに到達する高さの範囲まで行うことで造成される。
なお、竪孔51における残余部分、即ち、汚染土52が存在しない地層53に相当する部分については、拡径せずに締め固めてもよい。
Through the above-described backfilling step and compaction step, one creation step of the underground pile formed in a part of the height range where the contaminated soil 52 exists in the borehole 51 is completed. By repeating, the underground pile made of the underground pile forming mixed material C is formed so as to reach the height T1 where the contaminated soil 52 exists. That is, as shown in FIGS. 3 (f) to 3 (j), the second stage underground is obtained by refilling and compacting the hole 51 above the underground pile 54 a created by a single preparation process. At least contaminated soil 52 exists by creating the pile 54b, filling back the hole 51 above the second-stage underground pile 54b, and forming the third-stage underground pile 54c by compaction. The underground pile 54 expanded in diameter over the range of height can be created.
That is, the underground pile 54 is backfilled by introducing the underground pile formation mixed material C into the borehole 51 formed by excavating the boundary 52a on the underground side where the contaminated soil 52 exists. The catalyst D is injected into the mixed material for building underground piles C and compacted, and the diameter is expanded to form the first-stage underground pile 54a, and the underground pile forming mixed material is formed on the underground pile 54a. The material C is injected and backfilled, and the catalyst D is injected into the backfilled underground pile building material C to be compacted, and the hole 51 is expanded to form the second-stage underground pile 54b. The underground pile forming mixed material C is put on the underground pile 54b and backfilled, and the catalyst D is injected into the backfilled underground pile forming mixed material C to be compacted. The diameter of the hole 51 is expanded to create a third-stage underground pile 54c, and in this way, injection of the catalyst D and compaction of the underground pile-forming mixed material C are performed. It is Construction by performing one another to the height range to reach the surface side of the boundary 52b that is contaminated soil 52 present.
The remaining portion in the hole 51, that is, the portion corresponding to the formation 53 where the contaminated soil 52 does not exist may be compacted without being expanded in diameter.

図4は、汚染土壌50に対して複数の地中杭54を造成する場合において、当該汚染土壌50を平面視した場合の各地中杭54の位置関係を示す図である。
図4に示すように、竪孔51の孔径D1は汚染土壌50を平面視したときに、拡径後の竪孔同士がラップする孔径、すなわち、孔径D1の竪孔51を締め固めにより孔径D2に拡径して造成される地中杭54の拡径部分同士が重なるように汚染土壌50に対して各竪孔51を掘削する。具体的には、隣接する地中杭54の拡径部分同士が重なりを持って連続するように、汚染土52に対して千鳥状又は、方形状に地中杭54を複数造成して地中杭54が最も少なくなるように造成することで、汚染土壌50に立設された複数の地中杭54が汚染土52の存在する範囲において重なり合うため、汚染土52が存在する地層における平面視したときの単位面積あたりの地中杭が存在する割合が高まり、広範囲な浄化を効率的に行うことが可能となる。
また、汚染土壌50内に立設される複数の地中杭54が地中におけるフィルターのように作用するため、地中杭54が設けられた領域を地下水とともに汚染物質が通過することで、この汚染物質を浄化することができる。
FIG. 4 is a diagram showing the positional relationship of the various local piles 54 when the contaminated soil 50 is viewed in plan when a plurality of underground piles 54 are created with respect to the contaminated soil 50.
As shown in FIG. 4, when the contaminated soil 50 is viewed in plan, the hole diameter D1 of the dredging hole 51 is a hole diameter where the dredged holes wrap, that is, the hole diameter D2 by compacting the dredging hole 51 having the hole diameter D1. The boreholes 51 are excavated in the contaminated soil 50 so that the enlarged diameter portions of the underground piles 54 formed by expanding the diameter of the piles overlap each other. Specifically, a plurality of underground piles 54 are formed in a staggered or square shape with respect to the contaminated soil 52 so that the enlarged diameter portions of adjacent underground piles 54 are continuous with each other. Since the plurality of underground piles 54 erected on the contaminated soil 50 overlap in a range where the contaminated soil 52 exists, the piles 54 are formed in a plan view in the formation where the contaminated soil 52 exists. The proportion of underground piles per unit area increases, and a wide range of purification can be performed efficiently.
In addition, since the plurality of underground piles 54 standing in the contaminated soil 50 act like a filter in the ground, the contaminants pass through the region where the underground piles 54 are provided together with the groundwater. Contaminants can be purified.

なお、上記実施形態において、地中造成用土Bとして、竪孔51を形成する際に排出された排出土又は当該排出土とは別にあらかじめ用意された浄化済の砂や砕石が混ぜられた地中杭造成用の土としたが、排出土及びあらかじめ用意された浄化済の地中杭造成用の土を混合して地中造成用土Bとしても良い。
また、浄化反応を連鎖的に行わせる触媒Dとしての水酸化ナトリウムや水酸化カリウムは、埋め戻し後、締め固め前に注入することに限らず、スラストスクリュー17による締め固め中、又は、締め固め後に注入しても良い。
In addition, in the said embodiment, the underground in which the purified sand and the crushed stone prepared beforehand separately from the discharge soil discharged | emitted when forming the fistula 51 or the said discharge soil are mixed as the soil B for underground preparation Although it was set as the soil for pile construction, it is good also as soil B for underground creation by mixing discharge soil and the soil for underground pile preparation prepared previously.
Further, the sodium hydroxide or potassium hydroxide as the catalyst D for performing the purification reaction in a chain is not limited to being injected after the backfilling and before the compaction, but during the compaction by the thrust screw 17 or the compaction. It may be injected later.

実施形態2
上記実施形態1では、地中造成用土Bと浄化剤Aとしての粉体のアルカリ活性化過硫酸塩とが混合された地中杭造成用混合材Cを竪孔51内に投入して竪孔51を埋め戻し、触媒Dとしての水酸化ナトリウム又は水酸化カリウムを注入して締め固める工程を交互に行い、地中杭54を造成するとして説明したが、実施形態2では、浄化剤Aの粉体のアルカリ活性化過硫酸塩をキトサンやアルギン酸ナトリウム等の水溶性高分子によって被覆した浄化剤A′と地中造成用土Bとが予め混合された地中杭造成用混合材C′を竪孔51に投入して地中杭54を造成する。
本発明に係る浄化剤A′は、例えば、粉体の浄化剤Aを水溶性高分子からなる薄膜により所定量ずつ被包したものである。なお、浄化剤Aの被覆方法は、上記に限らず、水溶性高分子からなるカプセル内に密封しても良く、また、粉体の浄化剤Aを生成する過程で水溶性高分子によりコーティングしても良い。
Embodiment 2
In the first embodiment, the underground pile formation mixed material C in which the underground formation soil B and the powder alkali-activated persulfate as the purification agent A are mixed is introduced into the borehole 51 and the borehole is introduced. In the second embodiment, it is described that the underground pile 54 is formed by alternately filling back and filling 51 and injecting and compacting sodium hydroxide or potassium hydroxide as the catalyst D to form the underground pile 54. The ground pile mixing material C ′, in which the purification agent A ′, which is obtained by coating the alkali-activated persulfate of the body with a water-soluble polymer such as chitosan or sodium alginate, and the underground soil B, is pre-mixed. It is put into 51 and the underground pile 54 is created.
The purification agent A ′ according to the present invention is, for example, a powdery purification agent A encapsulated by a predetermined amount with a thin film made of a water-soluble polymer. The method of coating the purification agent A is not limited to the above, and it may be sealed in a capsule made of a water-soluble polymer, or coated with the water-soluble polymer in the process of producing the powder purification agent A. May be.

以下、本発明に係る実施形態2の地中杭54の造成方法について説明する。なお、竪孔51の形成までの工程については、実施形態1と同一のため、説明を省略する。本実施形態2では、実施形態1の埋め戻し工程において触媒Dの投入を行わない。
即ち、図3(f)乃至(j)に示すように、地中杭54は、汚染土52が存在する地中側の境界52aまでを掘削して形成した竪孔51に地中杭造成用混合材C′を投入して埋め戻し、この埋め戻された地中杭造成用混合材C′を締め固めるとともに拡径して一段目の地中杭54aを造成し、地中杭54aの上に地中杭造成用混合材C′を投入して埋め戻し、埋め戻された地中杭造成用混合材C′を締め固めるとともに竪孔51を拡径して二段目の地中杭54bを造成し、地中杭54bの上に地中杭造成用混合材C′を投入して埋め戻し、埋め戻された地中杭造成用混合材C′を締め固めるとともに竪孔51を拡径して三段目の地中杭54cを造成し、このように、地中杭造成用混合材C′の締め固めを交互に汚染土52が存在する地表側の境界52bに到達する高さの範囲まで行うことで地中杭54が造成される。
なお、竪孔51における残余部分の汚染土52が存在しない地層53に相当する部分については、拡径せずに締め固める。
Hereinafter, the creation method of the underground pile 54 of Embodiment 2 which concerns on this invention is demonstrated. In addition, since it is the same as that of Embodiment 1 about the process until formation of the fistula 51, description is abbreviate | omitted. In Embodiment 2, the catalyst D is not charged in the backfilling process of Embodiment 1.
That is, as shown in FIGS. 3 (f) to 3 (j), the underground pile 54 is used to create an underground pile in the borehole 51 formed by excavating the boundary 52 a on the underground side where the contaminated soil 52 exists. The mixed material C ′ is introduced and backfilled, and the backfilled underground pile formation mixed material C ′ is compacted and expanded to form a first-stage underground pile 54a. The underground pile formation mixed material C ′ is injected and backfilled, the backfilled underground pile formation mixed material C ′ is compacted, and the bore 51 is expanded to expand the second-stage underground pile 54b. The ground pile building mixture C 'is put on the underground pile 54b and backfilled, and the backfilled underground pile building mixture C' is compacted and the hole 51 is enlarged. Thus, the third-stage underground pile 54c is formed, and in this way, the ground pile-forming mixed material C ′ is compacted alternately on the surface side where the contaminated soil 52 exists. Ground pile 54 is reclamation by performing up to the height range to reach the field 52b.
The portion corresponding to the formation 53 in which the remaining contaminated soil 52 does not exist in the borehole 51 is compacted without expanding the diameter.

次に、図3(j)に示す工程の後に、図5(k)に示すように造成した地中杭54の中心を境界52aの深さまでボーリングし、細管25の一部が地層53の表面から突出するように、境界52aから地層53の表面まで地中杭54内に細管25を建て込み、図5(m)に示すように地表に突出する細管25の一部に液体供給手段20から延長されるチューブを接続し、流体供給手段20から供給される触媒Dを地中杭54内に注入する。
具体的には、境界52aから境界52bまでに地中杭54に建て込む細管25には、細管25の外周面を径方向に貫通する複数の孔25aが形成され、細管25内に供給される触媒Dを複数の孔25aから流出させて地中杭造成用混合材C′に浸透させる。つまり、触媒Dとしての水酸化ナトリウム又は水酸化カリウムが締め固められた地中杭造成用混合材C′を竪孔51内における汚染土が存在する高さまで到達させた後に投入される。
よって、触媒Dの供給よりも先に、浄化剤A′の薄膜が地中杭造成用混合材C′の水分と反応して溶解することにより、地中杭造成用混合材C′から造成されていない汚染土壌50に徐々に浄化剤Aが浸透する。そして、広範囲に渡り浸透した浄化剤Aに対して、細管25から供給され、地中杭造成用混合材C′内を浸透する触媒Dとが反応することにより、広範囲に渡り汚染土壌50が浄化される。
上記工程を汚染土壌50の浄化する範囲に行うことにより広範囲の汚染土壌50を確実に浄化することができるとともに地盤強化もすることができる。
Next, after the step shown in FIG. 3 (j), the center of the underground pile 54 formed as shown in FIG. 5 (k) is drilled to the depth of the boundary 52 a, and a part of the narrow tube 25 is the surface of the formation 53. From the boundary 52a to the surface of the formation 53, the narrow tube 25 is built in the underground pile 54, and the liquid supply means 20 is connected to a part of the narrow tube 25 protruding to the ground surface as shown in FIG. The extended tube is connected, and the catalyst D supplied from the fluid supply means 20 is injected into the underground pile 54.
Specifically, a plurality of holes 25a penetrating the outer peripheral surface of the thin tube 25 in the radial direction are formed in the thin tube 25 built in the underground pile 54 from the boundary 52a to the boundary 52b and supplied into the thin tube 25. The catalyst D is caused to flow out of the plurality of holes 25a and permeate into the underground pile building mixed material C ′. That is, the underground pile forming mixed material C ′, in which sodium hydroxide or potassium hydroxide as the catalyst D is compacted, is introduced after reaching the height where contaminated soil exists in the borehole 51.
Therefore, prior to the supply of the catalyst D, the thin film of the purifier A ′ reacts with the moisture of the underground pile building mixture C ′ to dissolve and is formed from the underground pile building mixture C ′. The cleaning agent A gradually permeates into the contaminated soil 50 that is not. Then, the contaminated soil 50 is purified over a wide area by reacting with the catalyst D supplied from the narrow tube 25 and permeating through the underground pile building mixture C ′ with respect to the purification agent A that has permeated over a wide area. Is done.
By performing the above-described process in a range where the contaminated soil 50 is purified, a wide range of contaminated soil 50 can be reliably purified and the ground can be strengthened.

図6は、広範囲に渡り上記工程により地中杭54を造成する場合の一例を示した図である。同図は、20m×20mの400mの範囲に対して、地中杭54の中心間距離が2mとなるように設定して造成する場合について示している。
この場合、図6に示すように、施工する地中杭54の総数は100本となり、1日当たりの施工工数を10本とすれば、全施工日数は10日を要することになる。
本発明に係る浄化剤A′と地中造成用土Bとが混合された地中杭造成用混合材C′を用いて地中杭54を造成することにより、まず、地盤強化をすることができる。次に、全ての地中杭54に対して同時に触媒Dを浸透させることにより、汚染土壌50の浄化を広範囲に渡り一度に施工することができる。
即ち、上記範囲の汚染土壌50の浄化及び地盤強化の施工1日目に造成された地中杭造成用混合材C′の浄化剤A′は、水溶性高分子により被覆されているので、直ちに全ての浄化剤Aが地中の水分と反応することなく、徐々に反応し、浄化剤Aが地中杭54内から造成されていない汚染土壌50にまで浸透する。これにより、施工完了の10日目までゆっくりと広範囲に浄化剤Aを浸透させることができる。
そして、全ての地中杭54の造成が完了した後に、地中杭54の全てに対して一度に触媒Dを注入することにより、地中杭造成用混合材C′から汚染土壌50まで触媒Dを浸透させて浄化剤Aと汚染物質とを反応させて一度に広範囲を浄化させることができる。
なお、触媒Dを注入する細管25を地中杭54に建て込むとして説明したが、互いに対角に位置する地中杭54の中心(図6の黒丸で示す点Pの位置)に細管25を建て込み、触媒Dを注入して、汚染土壌50の地中において触媒Dを浸透させて、浄化剤A′の溶解した薄膜部分から滲出する浄化剤Aを反応させるようにしても良い。このように細管25を建て込み、触媒Dを浸透させることにより、細管25を設ける工数を少なくすることができるので、工期を短縮することができる。
また、全範囲において地中杭54を境界52bまで造成した後に、地層53に開口する穴に触媒Dを投入し、重力方向に触媒Dを浸透させて、浄化剤A′と反応させても良い。この場合、触媒Dを供給するための細管を建て込む必要がないので工数をさらに抑制することができる。
即ち、本実施形態2によれば、浄化剤A′が水溶性高分子によりコーティングされたことにより、直ちに浄化剤A′が地中の水分と反応することがないので、浄化剤A′から浄化剤Aを徐々に滲出させて、浄化剤Aが汚染土壌50内を浸透する時間を設定することができる。よって、汚染土壌50の浄化の範囲が広範囲であっても、部分的に浄化したときのように浄化した領域が再び汚染されることを防止し、汚染土壌50に浄化されない領域の発生を防止できる。
FIG. 6 is a diagram showing an example in the case where the underground pile 54 is created by the above process over a wide range. This figure shows a case where the distance between the centers of the underground piles 54 is set to be 2 m with respect to a range of 400 m 2 of 20 m × 20 m.
In this case, as shown in FIG. 6, the total number of underground piles 54 to be constructed is 100, and if the number of construction man-hours per day is 10, the total construction days will require 10 days.
First, the ground can be strengthened by creating the underground pile 54 using the underground pile creation mixed material C ′ in which the purification agent A ′ and the underground creation soil B according to the present invention are mixed. . Next, by allowing the catalyst D to permeate all the underground piles 54 at the same time, the contaminated soil 50 can be purified over a wide range at once.
That is, the purification agent A ′ of the mixed material C ′ for underground pile construction, which was created on the first day of the purification of the contaminated soil 50 and the strengthening of the ground in the above range, is immediately covered with the water-soluble polymer. All the purification agent A reacts gradually without reacting with moisture in the ground, and the purification agent A penetrates from the inside of the underground pile 54 to the contaminated soil 50 that has not been created. Thereby, the purifier A can be permeated slowly over a wide range until the 10th day after the completion of construction.
Then, after the formation of all the underground piles 54 is completed, the catalyst D is injected into all of the underground piles 54 at a time, so that the catalyst D from the mixed material C ′ for underground pile formation to the contaminated soil 50 is obtained. The cleaning agent A and the pollutant are allowed to react with each other so that a wide range can be purified at once.
In addition, although it demonstrated that the thin tube 25 which inject | pours the catalyst D was built in the underground pile 54, the thin tube 25 was set in the center (position of the point P shown by the black circle of FIG. 6) of the underground pile 54 located mutually diagonally. The catalyst D may be injected, and the catalyst D may be permeated into the ground of the contaminated soil 50 to react with the purifier A leached from the thin film portion in which the purifier A ′ is dissolved. Thus, by installing the thin tube 25 and allowing the catalyst D to permeate, the number of steps for providing the thin tube 25 can be reduced, so that the work period can be shortened.
In addition, after the underground pile 54 is built up to the boundary 52b in the entire range, the catalyst D is put into a hole opened in the formation 53, and the catalyst D is allowed to permeate in the direction of gravity to react with the purifier A ′. . In this case, since it is not necessary to install a thin tube for supplying the catalyst D, the number of man-hours can be further reduced.
That is, according to the second embodiment, since the cleaning agent A ′ is coated with the water-soluble polymer, the cleaning agent A ′ does not immediately react with moisture in the ground, so that the cleaning agent A ′ is purified. The time during which the cleaning agent A permeates the contaminated soil 50 can be set by gradually exuding the agent A. Therefore, even if the range of purification of the contaminated soil 50 is wide, it is possible to prevent the area that has been purified from being contaminated again as when partially purified, and to prevent the generation of areas that are not purified by the contaminated soil 50. .

また、上記実施形態2において、浄化剤Aを薄膜で被包するとしたが、工期日程に応じて被包する薄膜の枚数を変えた浄化剤A′と地中造成用土Bとを混合し、地中杭造成用混合材C′を構成するようにしても良い。このように構成することにより、地中杭54の造成が全て完了して地盤強化した後に、触媒Dを浸透させ、汚染土壌50の全ての領域を一度に浄化することができる。
なお、汚染土壌に複数の地中杭を立設する場合においても、図4に示すように、竪孔の孔径は汚染土壌を平面視したときに拡径後の竪孔同士がラップする孔径で立設するようにしても良い。
In Embodiment 2 described above, the purifier A is encapsulated with a thin film. However, the purifier A ′ and the underground preparation soil B, in which the number of thin films to be encapsulated is changed according to the construction schedule, You may make it comprise the mixed material C 'for intermediate pile creation. By comprising in this way, after all the creation of the underground pile 54 is completed and ground reinforcement is carried out, the catalyst D can be penetrate | infiltrated and all the area | regions of the contaminated soil 50 can be purified at once.
In addition, even when standing a plurality of underground piles in the contaminated soil, as shown in FIG. 4, the hole diameter of the fistula is a hole diameter that the fistulas after diameter expansion wraps when the contaminated soil is viewed in plan. It may be erected.

以上、本発明を実施の形態を用いて説明したが、本発明の技術的範囲は上記実施の形態に記載の範囲には限定されない。上記実施の形態に、多様な変更または改良を加えることが可能である。   As mentioned above, although this invention was demonstrated using embodiment, the technical scope of this invention is not limited to the range as described in the said embodiment. Various modifications or improvements can be added to the above embodiment.

1 クレーン、11 ケーシング用オーガマシン、
12 インナースクリュー用オーガマシン、14 ケーシング、15 ホッパ、
16 シャフト、17 スラストスクリュー、18 貫通孔、20 流体供給手段、
50 汚染土壌、51 竪孔、52 汚染土、54 地中杭、
A;A′ 浄化剤、B 地中造成用土、C;C′ 地中杭造成用混合材。
1 crane, 11 auger machine for casing,
12 auger machine for inner screw, 14 casing, 15 hopper,
16 shaft, 17 thrust screw, 18 through hole, 20 fluid supply means,
50 contaminated soil, 51 fistula, 52 contaminated soil, 54 underground pile,
A: A ′ cleaning agent, B underground soil, C; C ′ mixed material for underground pile formation.

Claims (7)

汚染土壌に地中杭を立設して土壌を浄化する方法であって、
汚染土が存在する深さまで竪孔を掘削する工程と、
前記掘削により排出された排出土又はあらかじめ用意された地中杭造成用土と過硫酸ナトリウム、過硫酸カリウム、過硫酸アンモニウムのうちいずれかから選択されるアルカリ活性化過硫酸塩とが混合された地中杭造成用混合材を前記竪孔内に投入して竪孔を埋め戻す工程とを含み、
前記地中杭造成用混合材を前記竪孔内に投入した後に、水酸化ナトリウム又は水酸化カリウムを前記竪孔内に投入することを特徴とする汚染土壌浄化方法。
A method of purifying soil by setting up underground piles in contaminated soil,
Drilling a hole to a depth where contaminated soil exists;
The underground soil in which the discharged soil discharged by the excavation or a previously prepared soil for underground pile formation and an alkali activated persulfate selected from sodium persulfate, potassium persulfate, and ammonium persulfate are mixed And a step of filling the pile formation mixed material into the hole and backfilling the hole.
A contaminated soil purification method, wherein sodium hydroxide or potassium hydroxide is introduced into the borehole after the underground pile building mixed material is introduced into the borehole.
前記竪孔を埋め戻す工程は、前記竪孔内に貫入されたケーシング内に地中杭造成用混合材を投入し、当該地中杭造成用混合材を前記ケーシング内部のスラストスクリューの回転力で地中杭造成用混合材を前記竪孔内で締め固めることを特徴とする請求項1に記載の汚染土壌浄化方法。   In the step of refilling the borehole, the underground pile building mixed material is put into a casing penetrating into the borehole, and the underground pile building mixed material is moved by the rotational force of the thrust screw inside the casing. The contaminated soil purification method according to claim 1, wherein the underground pile building mixed material is compacted in the borehole. 前記アルカリ活性化過硫酸塩は、水溶性高分子により被覆されることを特徴とする請求項1又は請求項2に記載の汚染土壌浄化方法。   The contaminated soil purification method according to claim 1 or 2, wherein the alkali-activated persulfate is coated with a water-soluble polymer. 前記水酸化ナトリウム又は水酸化カリウムの投入と地中杭造成用混合材の締め固めとを交互に行い、当該締め固められた地中杭造成用混合材を前記竪孔内における汚染土が存在する高さまで到達させることを特徴とする請求項2に記載の汚染土壌浄化方法。   The introduction of the sodium hydroxide or potassium hydroxide and the compaction of the underground pile formation mixed material are alternately performed, and the ground soil pile mixed material is contaminated soil in the borehole. The contaminated soil purification method according to claim 2, wherein the method reaches the height. 前記水酸化ナトリウム又は水酸化カリウムは、締め固められた地中杭造成用混合材を前記竪孔内における汚染土が存在する高さまで到達させた後に投入することを特徴とする請求項3に記載の汚染土壌浄化方法。   The said sodium hydroxide or potassium hydroxide is thrown in after making the compacted underground pile formation mixed material reach the height where the contaminated soil exists in the borehole. Contaminated soil purification method. 前記締め固めにより、前記竪孔における前記汚染土が存在する高さの範囲を拡径することを特徴とする請求項2乃至請求項5いずれかに記載の汚染土壌浄化方法。   The contaminated soil purification method according to any one of claims 2 to 5, wherein a diameter range of the contaminated soil in the fistula is expanded by the compaction. 前記汚染土壌に複数の地中杭を立設する場合において、前記竪孔の孔径は汚染土壌を平面視したときに前記拡径後の竪孔同士がラップする孔径とすることを特徴とする請求項6に記載の汚染土壌浄化方法。   In the case where a plurality of underground piles are erected on the contaminated soil, the hole diameter of the fistula is set to a diameter that wraps the fistulas after the diameter expansion when the contaminated soil is viewed in plan. Item 7. A method for purifying contaminated soil according to Item 6.
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