JP2001129529A - Method for cleaning contaminated ground - Google Patents

Method for cleaning contaminated ground

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Publication number
JP2001129529A
JP2001129529A JP31538099A JP31538099A JP2001129529A JP 2001129529 A JP2001129529 A JP 2001129529A JP 31538099 A JP31538099 A JP 31538099A JP 31538099 A JP31538099 A JP 31538099A JP 2001129529 A JP2001129529 A JP 2001129529A
Authority
JP
Japan
Prior art keywords
purification
promoting component
contaminated ground
injection
well
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP31538099A
Other languages
Japanese (ja)
Other versions
JP3646589B2 (en
Inventor
Katsuhiko Kikuta
勝彦 菊田
Kensuke Fujii
研介 藤井
Hirokazu Tsuji
博和 辻
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Obayashi Corp
Original Assignee
Obayashi Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Obayashi Corp filed Critical Obayashi Corp
Priority to JP31538099A priority Critical patent/JP3646589B2/en
Publication of JP2001129529A publication Critical patent/JP2001129529A/en
Application granted granted Critical
Publication of JP3646589B2 publication Critical patent/JP3646589B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To provide a method for cleaning a contaminated ground by which a cleaning promoting component can be spread across a broad area to reach a faraway distance and thereby the cleaning power of the contaminated ground can be significantly upgraded and the component, especially costly decomposition microbes are recovered as much as possible even in an unsaturated zone and thus their recycling are feasible. SOLUTION: This method for cleaning a contaminated ground comprises a cleaning promoting component injection process to intermittently inject the cleaning promoting component, in a pulsed state and at an interval of short time, into a contaminated ground 12 under superhigh pressure from an injection well 14 inserted into an excavated well 13 formed by excavation in the contaminated ground 12, and a recovery/cleaning treating process to recover a gaseous substance by suction from the ground 12 through the well 13 and make the gaseous substance harmless by purifying treatment and discharge the harmless gaseous substance. These two processes are alternately repeated at every passage of specified time. In the recovery/cleaning treating process, the cleaning promoting component injected in the preceding cleaning promoting component injection process can be sucked back as much as possible. Thus it is possible to recover the decomposition microbes even in an unsaturated zone and recycle them.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、汚染地盤の浄化方
法に関し、特に、汚染地盤に挿入した注入井から超高圧
の空気を短時間の間隔でパルス状にして間欠的に汚染地
盤中に吹き込むだけでなく、汚染地盤中からガス状物質
を吸引回収するようにした汚染地盤の浄化方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for purifying a contaminated ground, and more particularly, to a method in which ultrahigh-pressure air is pulsed at short intervals from an injection well inserted into the contaminated ground and intermittently blown into the contaminated ground. In addition, the present invention relates to a method for purifying a contaminated ground in which gaseous substances are sucked and collected from the contaminated ground.

【0002】[0002]

【従来の技術】汚染物質として有機塩素系化合物および
油分、その他重金属類等様々の物質が挙げられ、更に、
これら汚染物質以外に有機性の分解成分を含めた汚染物
質等で汚染された地盤や廃棄物埋立地盤が大きな問題と
なっている。
2. Description of the Related Art Pollutants include various substances such as organochlorine compounds, oils, and other heavy metals.
Grounds and waste landfills contaminated with contaminants including organic decomposition components other than these contaminants have become a major problem.

【0003】このため、近年では上記汚染物質等の浄化
方法および浄化装置が各種提案されており、特に設備や
スペース上有利になる原位置浄化が多く見受けられる。
この原位置浄化では土着の分解微生物を利用する方法
(バイオレメディエーション)があり、この分解微生物
の活性化を図るために空気(酸素)や栄養塩類などの栄
養源を地盤中に注入したり、場合によっては新たに分解
微生物を補充したりすることが提案されている。例え
ば、特開平10−216696号公報には汚染土壌に酸
素を供給する装置が開示される。これは汚染土壌下の地
下水まで達する注入井を設け、この注入井から酸素を過
分に含む過飽和水を地下水中に供給して地下水を酸素過
飽和状態とし、この酸素過飽和の地下水から微細気泡を
発生させて表層の汚染土壌に酸素を供給しようとするも
のである。
For this reason, various methods and apparatuses for purifying the above contaminants have been proposed in recent years. In situ purification, which is particularly advantageous in terms of equipment and space, is often found.
In this in situ purification, there is a method (bioremediation) that utilizes indigenous decomposed microorganisms. In order to activate these decomposed microorganisms, nutrients such as air (oxygen) and nutrients are injected into the ground, In some cases, it has been proposed to replenish degrading microorganisms. For example, JP-A-10-216696 discloses a device for supplying oxygen to contaminated soil. This is to set up an injection well that reaches the groundwater under the contaminated soil, supply supersaturated water containing excess oxygen into the groundwater from the injection well, and turn the groundwater into an oxygen supersaturated state, and generate fine bubbles from this oxygen supersaturated groundwater. To supply oxygen to contaminated soil on the surface.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、かかる
従来の地下水から汚染土壌に酸素を供給する場合は、土
壌に酸素が自然に浸透することにより土着の分解微生物
が活性化されていくものであるから、著しく長い浄化期
間が必要になり、しかも土壌には割れ目や柔らかい箇所
があって全体に均一ではないので、このような箇所に酸
素が集中して浸透していってしまう結果、土壌全体を均
一に浄化することはできない。
However, when oxygen is supplied to contaminated soil from such conventional groundwater, indigenous decomposing microorganisms are activated by the natural infiltration of oxygen into the soil. However, it requires a very long purification period, and the soil has cracks and soft spots, which are not uniform. Can not be purified.

【0005】また、注入井を汚染土壌中に挿入して、酸
素(空気)あるいはその他の分解促進性物質および分解
微生物自体等の浄化促進成分を土壌中に直接注入するこ
とが考えられている。この場合、該浄化促進成分は水溶
液やガス状にして土壌中に注入することになるが、この
場合にあってもやはり土壌の不均一性により浄化ムラを
生ずる。また、注入に際しては、その注入圧を一定に保
って注入するが、連続的に注入するためにその注入圧も
高圧に設定することが困難であり、よって浄化促進成分
の到達距離は短く、これ故、注入井1基当たりの浄化可
能領域を広く確保することができない。従って、広範な
所望領域の汚染地盤を浄化するためには、注入井の本数
を多くしなければならず、地盤浄化のコストが高くなっ
てしまう。
It has also been considered that an injection well is inserted into contaminated soil, and oxygen (air) or other decomposition promoting substances and purification promoting components such as decomposition microorganisms themselves are directly injected into the soil. In this case, the purification-promoting component is injected into the soil in the form of an aqueous solution or gas, but even in this case, the purification is uneven due to the unevenness of the soil. In addition, at the time of injection, the injection pressure is maintained at a constant level. However, since the injection is performed continuously, it is difficult to set the injection pressure at a high pressure. Therefore, it is not possible to secure a wide purifiable area per injection well. Therefore, in order to purify the contaminated ground in a wide range of desired areas, the number of injection wells must be increased, and the cost of ground purification becomes high.

【0006】特に、汚染地盤の土壌が不飽和帯であっ
て、分解微生物その他の浄化促進成分を地盤中に拡散さ
せて運ぶ地下水がない場合には、分解微生物等の浄化促
進成分の移動は殆ど生じないので、上記浄化可能領域は
より一層狭まってしまう。また、このような不飽和帯に
分解微生物を注入井から注入するようにした場合には、
その分解微生物の移動は期待できないので、地下水とと
もに回収することもできず、これ故、分解微生物の再利
用が図れず、新たな分解微生物を注入し続けることが必
要になってしまい、かつ当該分解微生物は高価であるこ
とから、地盤浄化コストは大幅に高騰してしまうという
課題があった。
[0006] In particular, when the soil of the contaminated ground is in an unsaturated zone and there is no groundwater for dispersing decomposed microorganisms and other purification accelerating components into the ground, there is almost no movement of decomposed microorganisms and other decontamination accelerating components. Since this does not occur, the purifiable area is further reduced. Also, when degrading microorganisms are injected into such an unsaturated zone from an injection well,
Since the movement of the degrading microorganisms cannot be expected, it cannot be recovered together with the groundwater, so that the degrading microorganisms cannot be reused, and it is necessary to continuously inject new degrading microorganisms, and Since microorganisms are expensive, there is a problem that the cost of ground purification significantly rises.

【0007】本発明はかかる従来の課題に鑑みて成され
たものであり、その目的は、浄化促進成分をより遠くか
つより広範囲に到達させて汚染地盤の浄化能力を大幅に
向上させることが可能であり、しかも不飽和帯であって
も浄化促進成分、特に高価な分解微生物を可及的に回収
して再利用を可能とする汚染地盤の浄化方法を提供する
ことにある。
The present invention has been made in view of the above-mentioned conventional problems, and an object of the present invention is to make it possible to make a purification-promoting component farther and more widely, thereby greatly improving the purification ability of contaminated ground. Another object of the present invention is to provide a method for purifying contaminated ground, which makes it possible to recover and reuse a purification promoting component, particularly an expensive decomposed microorganism, as much as possible even in an unsaturated zone.

【0008】[0008]

【課題を解決するための手段】かかる目的を達成するた
めに本発明の汚染地盤の浄化方法は、汚染地盤に削孔し
た掘削井に超高圧をもって浄化促進成分を短時間の間隔
でパルス状にして間欠的に供給し、この掘削井からその
周囲の汚染地盤中に浄化促進成分を吹き込む浄化促進成
分注入工程と、該掘削井から地盤中のガス状物質を吸引
回収し、この回収したガス状物質を浄化処理により無害
化して排出する回収浄化処理工程とを有し、該浄化促進
成分注入工程と該回収浄化処理工程とを交互に繰り返す
ことを特徴とする(請求項1)。
In order to achieve the above object, a method for purifying a contaminated ground according to the present invention comprises the steps of forming a purification promoting component into a pulsed form at a short time interval at an extremely high pressure in a drilling well drilled in the contaminated ground. A purification-promoting component injecting step into the surrounding contaminated ground from the drilling well, and a gaseous substance in the ground being sucked and recovered from the drilling well. A recovery and purification treatment step of detoxifying and discharging the substance by a purification treatment, wherein the purification promoting component injection step and the recovery and purification treatment step are alternately repeated (claim 1).

【0009】この浄化方法では、浄化促進成分注入工程
にある掘削井には、浄化促進成分が超高圧(例えば2〜
10気圧)をもって短時間の間隔でパルス状にされて間
欠的(例えば、1/30〜1/5HZの周期)に供給されるた
め、該浄化促進成分は該掘削井から汚染地盤中に所定の
間欠タイミングをもって超高圧で爆発的に吹き込まれる
ことになる。このため、掘削井から汚染地盤中に注入さ
れる浄化促進成分はより遠くかつより広い範囲に拡散し
て到達されることになり、汚染地盤中の汚染物質を広範
囲に亘って浄化して、1基当たりの注入井での浄化領域
を大幅に拡大することが可能になる。また、浄化促進成
分の爆発的注入はパルス状にされて間欠的に継続して繰
り返されるため、注入の度に地盤の堆積状況に変化を及
ぼして浄化促進成分の通り道がランダムになり易く、地
盤全体を可及的にほぼ均一に浄化可能となる。更に、混
在する汚染物質等に適した浄化促進成分の注入を間欠注
入で実施することにより、注入成分の濃度の管理を容易
にして無駄が無くなる。
[0009] In this purification method, the drilling well in the step of injecting the purification-promoting component contains an ultra-high pressure (for example, 2 to 2).
10 atm) and supplied intermittently (for example, at a period of 1/30 to 1/5 HZ) at a short time interval, so that the purification promoting component is supplied from the drilling well into the contaminated ground in a predetermined manner. It will be explosively blown at ultra-high pressure with intermittent timing. For this reason, the purification promoting component injected into the contaminated ground from the drilling well is diffused and reaches a farther and wider area, and the contaminants in the contaminated ground are purified over a wide area, and 1 It is possible to greatly expand the purification area per injection well. In addition, since the explosive injection of the purification-promoting component is intermittently repeated in the form of a pulse, the path of the purification-promoting component is likely to be random at each injection, and the path of the purification-promoting component is likely to be random. The whole can be purified as uniformly as possible. Further, by intermittently injecting a purification promoting component suitable for mixed contaminants and the like, the concentration of the injected component can be easily controlled and waste can be eliminated.

【0010】また、回収浄化処理工程にある掘削井から
は、土壌の浄化時に発生する分解ガスや、上記注入井か
ら浄化促進成分をガス(霧)状にして注入した際の余剰
ガス、および土壌中の水分等が吸引される。このため、
不飽和帯の土壌であっても、その前工程の浄化促進成分
注入工程で注入した浄化促進成分をガス状物質とともに
可及的に回収できるようになり、特に、高価である分解
微生物を回収再利用することで、地盤浄化コストの可及
的な低減化が図れるようになる。
[0010] In addition, from the drilling well in the recovery and purification treatment step, decomposition gas generated at the time of soil purification, surplus gas when a purification promoting component is injected in the form of gas (mist) from the injection well, and soil The moisture and the like in the interior are sucked. For this reason,
Even in soils in unsaturated zones, it is possible to recover as much as possible the purification-promoting components injected together with the gaseous substances in the purification-promoting-component injection process in the preceding process. By using this, the ground purification cost can be reduced as much as possible.

【0011】加えて、浄化促進成分注入工程と回収浄化
処理工程とを切り替える場合に、隣接する工程の異なる
掘削井相互間で、注入井と吸引手段とを付け替えるだけ
で済み、工程移行が容易に行え、施工性に優れる。
In addition, when switching between the purification promoting component injection step and the recovery / purification treatment step, it is only necessary to change the injection well and the suction means between the drilling wells in different adjacent steps, and the process can be easily shifted. It can be performed and has excellent workability.

【0012】ここで、前記掘削井は複数設け、浄化促進
成分注入工程にある掘削井に隣接する掘削井は回収浄化
処理工程となすことが望ましい(請求項2)。
Here, it is preferable that a plurality of the drilling wells are provided, and a drilling well adjacent to the drilling well in the purification promoting component injection step is a recovery and purification treatment step (claim 2).

【0013】この浄化方法では、浄化促進成分注入工程
の掘削井から浄化促進成分を汚染地盤中に注入する一方
で、その周囲に隣接する回収浄化処理工程の掘削井から
ガス状物質を吸引するので、浄化促進成分がより拡散し
易くなるとともに、分解ガスや余剰ガス等の有害なガス
状物質が地盤から自然に大気中に放出される前に、これ
らを吸引井で捕集して浄化処理した後に放出できるた
め、大気汚染を可及的に防止することができる。
According to this purification method, while the purification promoting component is injected into the contaminated ground from the drilling well in the purification promoting component injection step, the gaseous substance is sucked from the drilling well in the recovery purification processing step adjacent to the surrounding area. Before the harmful gaseous substances such as decomposed gas and surplus gas are naturally released from the ground to the atmosphere, these substances are collected and purified by a suction well, and the purification promoting components are more easily diffused. Since it can be released later, air pollution can be prevented as much as possible.

【0014】また、上記浄化促進成分には、空気や過酸
化水素やオゾン等の酸素含有物質、分解微生物、分解微
生物を活性化する栄養源、などの汚染物質の浄化を促進
する成分を用いることができ、各種汚染物質に即した浄
化を適正に行うことができる(請求項3)。
Further, as the above-mentioned purification promoting component, a component which promotes the purification of pollutants such as oxygen-containing substances such as air, hydrogen peroxide and ozone, decomposing microorganisms, and nutrients for activating the decomposing microorganisms is used. Thus, it is possible to appropriately perform purification in accordance with various pollutants (claim 3).

【0015】さらに、上記掘削井の内周には多孔質管を
配置して、前記浄化促進成分注入工程では、該多孔質管
内部に、先端に噴出口を有するとともに該噴出口の上側
に該多孔質管に密接してシールするパッカーが取り付け
られた注入井を挿入して、該噴出口から前記浄化促進成
分を間欠供給する一方、前記回収浄化処理工程では、該
多孔質管の上端部に吸引手段を備えた回収浄化処理設備
を接続してガス状物質を吸引回収することが望ましい
(請求項4)。
Further, a porous pipe is arranged on the inner periphery of the drilling well, and in the step of injecting the purification promoting component, the porous pipe has a spout at a tip and a spout at an upper side of the spout. Inserting an injection well fitted with a packer that seals tightly to the porous tube, and intermittently supplies the purification promoting component from the jet port. It is desirable to connect a recovery and purification treatment facility equipped with a suction means to suction and recover gaseous substances (claim 4).

【0016】この浄化方法では、1つの掘削井での浄化
促進成分の注入位置を上下に変化させて調整することが
できるため、汚染地盤の汚染領域の深度が大きい場合に
も浄化促進成分を上下方向に均等に吹き込んで、地盤の
浄化を上下方向に均等化することができる。また、浄化
促進成分注入工程と回収浄化処理工程との工程移行を行
う際に、注入井と吸引手段を備えた回収浄化処理設備と
の付け替え作業が簡易に行え、工程移行の作業性に優れ
る。
In this purification method, since the injection position of the purification promoting component in one drilling well can be adjusted by changing the position up and down, even if the depth of the contaminated region of the contaminated ground is large, the purification promoting component can be adjusted up and down. In this case, the ground can be evenly blown in the direction, so that the purification of the ground can be equalized in the vertical direction. Further, when performing the process transition between the purification promoting component injecting step and the recovery and purification processing step, the work of replacing the recovery and purification processing equipment with the injection well and the suction means can be easily performed, and the workability in the process transition is excellent.

【0017】[0017]

【発明の実施の形態】以下、本発明の実施形態を添付図
面を参照して詳細に説明する。図1は本発明の汚染地盤
の浄化方法の第1実施形態を示し、同図は浄化装置の要
部を概略的に示す断面図である。
Embodiments of the present invention will be described below in detail with reference to the accompanying drawings. FIG. 1 shows a first embodiment of a method for purifying contaminated ground according to the present invention, and FIG. 1 is a sectional view schematically showing a main part of a purification apparatus.

【0018】本発明の汚染地盤の浄化方法の基本とする
ところは、汚染地盤12に掘削形成した掘削井13に超
高圧をもって浄化促進成分を短時間の間隔でパルス状に
して間欠的に供給し、この掘削井13からその周囲の汚
染地盤12中に浄化促進成分を高圧で所定の間欠タイミ
ングをもって爆発的に吹き込む浄化促進成分注入工程
と、当該掘削井13から地盤中12のガス状物質を吸引
回収し、この回収したガス状物質を浄化処理により無害
化して排出する回収浄化処理工程とを有して、これら浄
化促進成分注入工程と回収浄化処理工程とを交互に繰り
返すことにある。
The basis of the method for purifying a contaminated ground according to the present invention is based on the fact that a purification promoting component is intermittently supplied at short intervals to a drilling well 13 formed in a contaminated ground 12 at an extremely high pressure. A step of injecting a purification-promoting component explosively from the drilling well 13 into the surrounding contaminated ground 12 at a high pressure at a predetermined intermittent timing; The present invention has a recovery and purification treatment step of recovering and detoxifying and recovering the collected gaseous substances by a purification treatment, and the purification promotion component injection step and the recovery and purification treatment step are alternately repeated.

【0019】即ち、本発明の汚染地盤の浄化方法は図1
に示す浄化装置10をもって達成できる。この浄化装置
10は本発明の浄化方法を達成するための一実施形態を
示し、汚染地盤12に略鉛直に掘孔されて内周部に土留
め用としての多孔質管30が嵌入配置された掘削井13
と、この掘削井13内部に挿入される注入井14と、こ
の注入井14の上端部に取り付けられて超高圧の圧搾空
気を短時間の間隔でパルス状にして間欠的に該注入井1
4に供給する高圧間欠注入装置16と、該圧搾空気の供
給経路18に接続され浄化促進成分を圧搾空気に添加す
る浄化促進成分供給設備20、並びに上記注入井14に
付け替えられて掘削井13の多孔質管30の上端部にカ
ップリングなどを介して接続される吸引ポンプ34など
からなる回収浄化処理設備40とを備えて構成される。
That is, the method for purifying contaminated ground of the present invention is shown in FIG.
Can be achieved by the purifying apparatus 10 shown in FIG. This purification apparatus 10 shows one embodiment for achieving the purification method of the present invention, and is formed by digging a substantially vertical hole in the contaminated ground 12, and a porous tube 30 for earth retaining is inserted into the inner peripheral portion. Drilling well 13
And an injection well 14 inserted into the drilling well 13, and an ultrahigh-pressure compressed air attached to the upper end of the injection well 14 is pulsed at short intervals to intermittently fill the injection well 1.
4, a high-pressure intermittent injection device 16 for supplying to the compressed air, a purification-promoting component supply facility 20 connected to the compressed air supply path 18 for adding the purification-promoting component to the compressed air, and a drilling well 13 A recovery / purification treatment facility 40 including a suction pump 34 connected to the upper end of the porous tube 30 via a coupling or the like is provided.

【0020】上記多孔質管30は、その下端部から上方
部分が所定の長さに亘って周面にスリットや孔等でなる
無数の開口が形成されたパイプでなり、当該開口形成部
位が汚染地盤12中の汚染物質の拡散層Sに挿入され
て、汚染地盤12の所定深度まで達し、上端部は地表よ
り突出している。
The porous tube 30 is a pipe having an infinite number of openings formed by slits, holes, and the like formed on a peripheral surface of the porous tube 30 from a lower end to an upper portion over a predetermined length. It is inserted into the contaminant diffusion layer S in the ground 12, reaches a predetermined depth of the contaminated ground 12, and its upper end protrudes from the surface of the ground.

【0021】また、掘削井13内に挿入される注入井1
4は上記多孔質管30より短めの所定長さのパイプで形
成され、これの下端部に設けられる噴出口14aは汚染
地盤12の所定深度に位置するとともに、該注入井14
の上端部は多孔質管30の上端部より更に上方に突出し
た状態にある。
The injection well 1 inserted into the drilling well 13
4 is formed of a pipe having a predetermined length shorter than the porous pipe 30, and an ejection port 14 a provided at a lower end thereof is located at a predetermined depth of the contaminated ground 12, and the injection well 14 a
Is in a state protruding further above the upper end of the porous tube 30.

【0022】上記高圧間欠注入装置16は上記注入井1
4の上端にカップリングを介して接続され、該高圧間欠
注入装置16にはエアコンプレッサ22で発生される超
高圧(例えば、2〜10気圧)の圧搾空気が供給管18
aを介して導入される。該高圧間欠注入装置16は、図
示省略したが圧搾空気を貯留するタンクと、このタンク
内の圧搾空気を間欠的に排出する間欠バルブとを備え、
タンク内の圧力が所定圧以上になると間欠バルブが瞬時
に開弁して高圧空気を排出するとともに、この排出によ
ってタンク内圧力が低下されると間欠バルブは瞬時に閉
弁される構造となっている。
The high-pressure intermittent injection device 16 is connected to the injection well 1
4 is connected via a coupling to the high-pressure intermittent injection device 16, and compressed air of an ultra-high pressure (for example, 2 to 10 atm) generated by an air compressor 22 is supplied to a supply pipe 18.
a. The high-pressure intermittent injection device 16 includes a tank (not shown) that stores compressed air, and an intermittent valve that intermittently discharges compressed air in the tank,
When the pressure in the tank exceeds a predetermined pressure, the intermittent valve opens instantaneously to discharge high-pressure air, and when the pressure in the tank decreases due to this discharge, the intermittent valve closes instantly. I have.

【0023】従って、エアコンプレッサ22から圧搾空
気が供給される間は、高圧間欠注入装置16はタンク内
の高圧空気を短時間の間隔でパルス状にして間欠的(例
えば、1/30〜1/5HZの周期)に排出し続け、この圧搾空
気は上記注入井14に供給される。すると、この超高圧
の圧搾空気は注入井14の下端部の噴出口14aから所
定の間欠タイミングをもって瞬間的に掘削井13の多孔
質管30を通じて周囲の汚染地盤12中に注入される。
この注入の際、キャビテーション効果が発揮されて圧搾
空気は爆発的に多孔質管30の無数の孔から吹き出さ
れ、このときの吹き出しエネルギーは著しく大きなもの
となる。
Therefore, while the compressed air is supplied from the air compressor 22, the high-pressure intermittent injection device 16 intermittently changes the high-pressure air in the tank into pulses at short intervals (for example, 1/30 to 1/30). The compressed air is supplied to the injection well 14. Then, the compressed air of the ultra-high pressure is instantaneously injected into the surrounding contaminated ground 12 through the porous pipe 30 of the drilling well 13 from the jet port 14a at the lower end of the injection well 14 at a predetermined intermittent timing.
At the time of this injection, the cavitation effect is exerted, and the compressed air is explosively blown out from the myriad of holes of the porous tube 30, and the blowing energy at this time becomes extremely large.

【0024】上記浄化促進成分供給設備20としては、
浄化促進成分を溜める貯蔵タンク24が設けられ、この
貯蔵タンク24は流量調整バルブ26を介して管路24
aで高圧間欠注入装置16の吐出側の供給経路18に連
通される。ここで供給経路18とは、圧搾空気をエアコ
ンプレッサ22から汚染地盤12中に供給する経路であ
り、該エアコンプレッサ22と高圧間欠注入装置16と
を結ぶ上記供給管18a、および該高圧間欠注入装置1
6自体、更に、注入井14を含むものとする。そして、
該流量調整バルブ26を開弁することにより、貯蔵タン
ク24内の浄化促進成分は圧搾空気中に添加され、か
つ、この添加量は該流量調整バルブ26の開度調節によ
り制御される。
The above-mentioned purification promoting component supply equipment 20 includes:
A storage tank 24 for storing the purification promoting component is provided, and this storage tank 24 is connected to a pipe 24 through a flow control valve 26.
At a, it is connected to the supply path 18 on the discharge side of the high-pressure intermittent injection device 16. Here, the supply path 18 is a path for supplying compressed air from the air compressor 22 into the contaminated ground 12, and the supply pipe 18a connecting the air compressor 22 and the high-pressure intermittent injection device 16, and the high-pressure intermittent injection device. 1
6 itself further includes an injection well 14. And
By opening the flow control valve 26, the purification promoting component in the storage tank 24 is added to the compressed air, and the amount of addition is controlled by adjusting the opening of the flow control valve 26.

【0025】上記貯蔵タンク24に溜められる浄化促進
成分は、空気や過酸化水素(H22)やオゾン(O3
等の酸素含有物質、分解微生物M、この分解微生物Mを
活性化させる栄養源、などの汚染物質の浄化を促進する
成分である。汚染物質は特に代表的なものとして有機塩
素系化合物、油、溶剤、揮発性物質等がある。
The purification accelerating components stored in the storage tank 24 are air, hydrogen peroxide (H 2 O 2 ), ozone (O 3 )
It is a component that promotes purification of contaminants such as oxygen-containing substances such as oxygen-decomposing microorganisms M, nutrients for activating the decomposed microorganisms M, and the like. The contaminants include, in particular, organochlorine compounds, oils, solvents, and volatile substances.

【0026】空気はこれに含まれる酸素により好気性微
生物Mの活性化を促進し、H22は酸素を発生するとき
の気泡により油汚染土の土粒子より油を剥離する効果が
あり、水と酸素に分解した後は余分な物質が残留せず、
かつ、霧状として容易に注入できる。また、O3は酸化
効率が更に良い。栄養源は、分解微生物Mを増殖するに
適した栄養塩類やこの分解微生物Mを活性化するに適し
た成分が用いられ、例えば、栄養塩類としては、燐,窒
素,カリ,珪素など生物の生命を維持するうえで必要な
主要元素と、マンガンなどの微量元素で炭素、水素、酸
素以外の主に塩類として摂られるものがある。
The air promotes the activation of the aerobic microorganisms M by the oxygen contained therein, and H 2 O 2 has the effect of separating oil from the soil particles of the oil-contaminated soil by bubbles when generating oxygen, After decomposing into water and oxygen, no extra substances remain,
And it can be easily injected as a mist. O 3 has better oxidation efficiency. As the nutrient source, nutrients suitable for growing the degrading microorganism M and components suitable for activating the degrading microorganism M are used. Examples of the nutrient include phosphorus, nitrogen, potash, silicon, and the like of living organisms. There are some major elements required to maintain the above and trace elements such as manganese which are mainly taken as salts other than carbon, hydrogen and oxygen.

【0027】また、分解微生物MとしてはTCE(トリ
クロロエチレン)を好気分解(酸化)するメタン資化性
菌が知られるが、このメタン資化性菌では栄養源として
メタンが用いられる。また、TCE分解に用いられるそ
の他の分解微生物Mとしては、トルエン資化性菌、フェ
ノール資化性菌、硝化細菌、プロパン酸化細菌、イソプ
ロピレン酸化細菌などが知られ、それぞれに適した栄養
源が用いられる。勿論、TCEに限ることなく汚染地盤
12中のその他の汚染物質に対しては、その汚染物質を
浄化する分解微生物Mに適した栄養源が用いられること
はいうまでもない。
As the decomposing microorganism M, a methane-utilizing bacterium which aerobically decomposes (oxidizes) TCE (trichloroethylene) is known. In this methane-utilizing bacterium, methane is used as a nutrient source. Other decomposing microorganisms M used for TCE decomposition include toluene-utilizing bacteria, phenol-utilizing bacteria, nitrifying bacteria, propane-oxidizing bacteria, and isopropylene-oxidizing bacteria. Used. It goes without saying that a nutrient source suitable for the decomposing microorganism M that purifies the contaminant is used for other contaminants in the contaminated ground 12 without being limited to the TCE.

【0028】従って、上記浄化装置10のエアコンプレ
ッサ22を駆動して圧搾空気を高圧間欠注入装置16に
供給して、この超高圧の圧搾空気を注入井14の噴出口
14aから掘削井13の多孔質管30を通じて周囲の汚
染地盤12中に注入するときに、浄化促進成分供給設備
20の流量調整バルブ26を開弁しておくことによっ
て、貯蔵タンク26内の浄化促進成分を上記圧搾空気と
ともに汚染地盤12中に注入し得る。ここで、酸素を含
む圧搾空気は浄化促進成分の1つであり、以下、該圧搾
空気を含めて浄化促進成分として表現する。
Accordingly, the air compressor 22 of the purification device 10 is driven to supply compressed air to the high-pressure intermittent injection device 16, and this ultra-high pressure compressed air is supplied from the injection port 14 a of the injection well 14 to the hole of the drilling well 13. By opening the flow control valve 26 of the purification promoting component supply facility 20 when injecting into the surrounding contaminated ground 12 through the quality pipe 30, the purification promoting component in the storage tank 26 is contaminated together with the compressed air. It can be injected into the ground 12. Here, the compressed air containing oxygen is one of the purification-promoting components, and is hereinafter referred to as the purification-promoting component including the compressed air.

【0029】そして、汚染地盤12中に注入される浄化
促進成分は、上記高圧間欠注入装置16によって超高圧
をもって短時間の間隔でパルス状にされて所定の間欠タ
イミングで供給されるため、多孔質管30の無数の開口
より汚染地盤12中に爆発的に吹き込まれ、より遠くか
つより広範囲に到達されることになる。また、上記浄化
促進成分の爆発的注入は間欠的に繰り返されるため、注
入の度に汚染地盤12の堆積状況に変化を及ぼして浄化
促進成分の通り道がランダムになり易く、汚染地盤12
全体がほぼ均一に浄化される。更に、上記流量調整バル
ブ26の開度調整により浄化促進成分の流量制御が可能
となるが、混在する汚染物質等に適した浄化促進成分の
注入を間欠注入で実施することにより、間欠注入成分の
濃度の管理を容易にして無駄が無くなる。
The purification-promoting component injected into the contaminated ground 12 is pulsed at short intervals at an ultra-high pressure by the high-pressure intermittent injection device 16 and supplied at a predetermined intermittent timing. Explosive blowing into the contaminated ground 12 through the myriad openings in the tube 30 will result in reaching farther and more extensively. In addition, since the explosive injection of the purification promoting component is intermittently repeated, the deposition condition of the contaminated ground 12 changes every time the injection is performed, so that the path of the purification promoting component tends to become random, and the contamination ground 12
The whole is almost uniformly purified. Further, the flow rate of the purification promoting component can be controlled by adjusting the opening degree of the flow control valve 26. However, by performing the injection of the purification promoting component suitable for the mixed pollutants by intermittent injection, the intermittent injection component can be controlled. The concentration can be easily managed and waste can be eliminated.

【0030】このように汚染地盤12に注入された浄化
促進成分はより広範囲に拡散されるため、1基当たりの
注入井14での浄化領域を拡大することができ、一定の
領域の汚染地盤の浄化を行うには浄化装置10全体の注
入井14の本数を減らすことができる。つまり、浄化促
進成分は、空気に含まれる酸素や栄養源により汚染地盤
12中に含まれる分解微生物Mを広範囲で活性化して、
汚染物質の分解を促進する。また、分解微生物Mを用い
るにあたり、汚染対象がその浄化期間が長期化される油
や溶剤や揮発性物質である場合には、それぞれの浄化に
適した浄化促進成分を選択しておくことにより、これら
汚染物質を短期間のうちに適正に浄化できる。更に、土
着の分解微生物Mが少ない場合は、浄化促進成分として
補充用の分解微生物Mを含めることが望ましい。
As described above, the purification-promoting component injected into the contaminated ground 12 is diffused over a wider area, so that the purifying area per injection well 14 per unit can be expanded, and the contaminated ground in a certain area can be reduced. To perform purification, the number of injection wells 14 in the entire purification apparatus 10 can be reduced. In other words, the purification promoting component activates the decomposing microorganisms M contained in the contaminated ground 12 in a wide range by oxygen and nutrients contained in the air,
Promotes decomposition of pollutants. Further, in using the degrading microorganism M, if the polluted object is an oil, a solvent, or a volatile substance whose purification period is lengthened, by selecting a purification promoting component suitable for each purification, These contaminants can be properly purified within a short period of time. Furthermore, when the amount of indigenous decomposed microorganisms M is small, it is desirable to include replenished decomposed microorganisms M as a purification promoting component.

【0031】また、この実施形態の浄化方法を達成する
ための浄化装置10は、地盤12中のガス状物質を吸引
するための吸引井31が併設されて構成される。この吸
引井31は上記掘削井13にて形成され、掘削井13の
多孔質管30の上端部にカップリングを介して吸引ポン
プ34を備えた回収浄化処理設備40が繋がれることで
構成される。この回収浄化処理設備40は気液分離装置
32、吸引ポンプ34、排出ガス浄化装置36、浄化ガ
ス排気設備38とからなり、当該回収浄化処理設備40
と前記高圧間欠注入装置16とは掘削井13の多孔質管
30に対して適宜に付け替え及び接続替えされるように
なっていて、各掘削井13は注入井14および吸引井3
1の双方として機能し得るようになっており、図2の
(a)と(b)とに示すように、各掘削井13は浄化促
進成分注入工程と回収浄化処理工程とが交互に繰り返さ
れて行われるようになっている。また、この回収浄化処
理設備40に繋がれて回収浄化処理工程を行う吸引井1
4と、高圧間欠注入装置16が接続されて浄化促進処理
工程が行われる注入井14とは、図示していないが、平
面視で相互に取り囲むようにして複数配置され、隣接す
るもの同士は互いに異なった工程の注入井14および吸
引井14となっている。
The purifying apparatus 10 for achieving the purifying method of this embodiment is provided with a suction well 31 for sucking gaseous substances in the ground 12. The suction well 31 is formed by the drilling well 13, and is configured by connecting a recovery and purification treatment facility 40 having a suction pump 34 to the upper end of the porous tube 30 of the drilling well 13 via a coupling. . The recovery and purification equipment 40 comprises a gas-liquid separator 32, a suction pump 34, an exhaust gas purification device 36, and a purified gas exhaust equipment 38.
And the high-pressure intermittent injection device 16 are appropriately replaced and connected to the porous pipe 30 of the drilling well 13. Each of the drilling wells 13 includes the injection well 14 and the suction well 3.
As shown in FIGS. 2A and 2B, each drilling well 13 alternately repeats a purification promoting component injection step and a recovery purification treatment step. Is performed. Further, the suction well 1 which is connected to the recovery / purification processing equipment 40 and performs the recovery / purification processing step.
4 and a plurality of injection wells 14 to which the high-pressure intermittent injection device 16 is connected to perform the purification promotion processing step, which are not shown, are arranged so as to surround each other in plan view, and adjacent ones are mutually connected. An injection well 14 and a suction well 14 of different processes are provided.

【0032】そして、該吸引ポンプ34を稼働すること
により、上記吸引井31の開口部からは、土壌の浄化時
に発生する分解ガスや、上記注入井14から浄化促進成
分をガス(霧)状にして注入した際の余剰ガス、および
土壌中の水分等が吸引される。このように吸引井31で
吸引された水分混じりのガス状物質は、気液分離装置3
2で分離された後にガスのみが該吸引ポンプ34に吸引
される。そして、吸引ポンプ34で吸引されたガスは排
出ガス浄化装置36に送り込まれ、ここでガスは浄化処
理されて無害化された後に、浄化ガス排気設備38から
大気中に放出される。
By operating the suction pump 34, the decomposition gas generated during soil purification and the purification promoting component from the injection well 14 are formed into a gas (mist) from the opening of the suction well 31. Excess gas and water in the soil at the time of injection are sucked. The gaseous substance mixed with water sucked in the suction well 31 in this manner is supplied to the gas-liquid separator 3.
After the separation in step 2, only the gas is sucked into the suction pump 34. Then, the gas sucked by the suction pump 34 is sent to the exhaust gas purifying device 36, where the gas is purified and rendered harmless, and then released into the atmosphere from the purified gas exhaust system 38.

【0033】即ち、注入井14が挿入された浄化促進成
分注入工程の掘削井13からは浄化促進成分を汚染地盤
12中に注入する一方、その周囲に隣接して回収浄化処
理設備40に繋がれた回収浄化処理工程の掘削井13か
らはガス状物質を吸引するので、浄化促進成分がより拡
散し易くなるとともに、分解ガスや余剰ガス等の有害な
ガス状物質が地盤から自然に大気中に放出される前に、
これらを吸引井31で捕集して浄化処理した後に放出で
きるため、大気汚染を可及的に防止することができる。
That is, while the purification promoting component is injected into the contaminated ground 12 from the drilling well 13 in the purification promoting component injection step into which the injection well 14 has been inserted, the recovery promoting purification equipment 40 is connected adjacent to the periphery thereof. Since the gaseous substance is sucked from the drilling well 13 in the recovery and purification treatment step, the purification promoting component is more easily diffused, and harmful gaseous substances such as decomposition gas and surplus gas are naturally discharged from the ground to the atmosphere. Before being released,
Since these can be collected and collected in the suction well 31 and then released, the air pollution can be prevented as much as possible.

【0034】ところで、本実施形態の浄化方法では、各
掘削井13に対し、その多孔質管30に注入井14を挿
入して浄化促進成分を注入する浄化促進成分注入工程
と、その多孔質管30に回収浄化処理設備40を繋いで
吸引回収したガス状物質を浄化して排出する回収浄化処
理工程とが所定時間を経過する毎に切り替えられて交互
に繰り返される。そして、この工程の切り替えは、隣接
して互いに工程の異なる掘削井13,13…同士で、注
入井14と回収浄化処理設備との付け替えを行うことに
よってなされる。従って、この工程の切り替えのための
作業は上記付け替えを行うだけで簡易に行うことができ
る。
By the way, in the purification method of the present embodiment, for each excavation well 13, a purification promotion component injection step of inserting the injection well 14 into the porous tube 30 and injecting the purification promotion component, The recovery and purification process step of purifying and discharging the gaseous substance sucked and recovered by connecting the recovery and purification processing facility 40 to the recovery purification process unit 40 is switched and repeated alternately every predetermined time. The switching of the process is performed by exchanging the injection well 14 with the recovery and purification treatment equipment between the adjacent drilling wells 13 having different processes. Therefore, the work for switching the process can be easily performed only by performing the replacement.

【0035】従って、この実施形態の浄化方法では注入
井14から浄化促進成分を汚染地盤12中に注入する一
方、吸収井31から吸引するので、この吸引により注入
井14から供給される浄化促進成分がより拡散し易くな
る。このため、上記注入井14から高圧間欠注入装置1
6を介して浄化促進成分が爆発的に吹き込まれることと
相俟って、浄化可能領域を著しく拡大することができ
る。
Therefore, in the purification method of this embodiment, the purification promoting component is injected into the contaminated ground 12 from the injection well 14 and is sucked from the absorption well 31. Therefore, the purification promoting component supplied from the injection well 14 by this suction. Are more easily diffused. Therefore, the high-pressure intermittent injection device 1
In combination with the explosive blowing of the purification-promoting component via 6, the purifiable area can be significantly expanded.

【0036】また、汚染地盤12中の分解ガスや余剰ガ
スが自然に大気中に放出される前に上記吸引井30で捕
集することができるため、大気汚染を防止することがで
きる。従って、この実施形態では汚染地盤12の浄化・
安定化が短期間のうちに行われるため、特に早期の跡地
利用や環境保全に有益であるとともに、周辺環境に配慮
することができる。
Further, since the decomposition gas and surplus gas in the contaminated ground 12 can be collected by the suction well 30 before being naturally released to the atmosphere, air pollution can be prevented. Therefore, in this embodiment, purification of the contaminated ground 12
Since the stabilization is performed within a short period of time, it is particularly useful for early use of the site and environmental conservation, and the surrounding environment can be considered.

【0037】更に、各掘削井13は浄化促進成分注入工
程と回収浄化処理工程とが所定時間を経過する毎に切り
替えられて、これらの工程を順次交互に繰り返すことに
なるので、回収浄化処理工程にある掘削井からは、土壌
の浄化時に発生する分解ガスや、上記注入井14から浄
化促進成分をガス(霧)状にして注入した際の余剰ガ
ス、および土壌中の水分等を吸引回収するにあたって、
その汚染地盤の土壌が不飽和帯であっても、その前工程
の浄化促進成分注入工程で注入した浄化促進成分をガス
状物質とともに可及的に回収できるようになり、特に、
高価である分解微生物を回収再利用することで、地盤浄
化コストの可及的な低減化が図れるようになる。なお、
気液分離装置32で分離された水分は戻し配管32aに
よって貯蔵タンク24に戻されるようになっており、こ
の気液分離された水分とともに回収した分解微生物は貯
蔵タンクに戻される。
Further, in each of the drilling wells 13, the purification promoting component injection step and the recovery purification processing step are switched every time a predetermined time elapses, and these steps are sequentially and alternately repeated. From the drilling well, the decomposition gas generated at the time of soil purification, the excess gas when the purification promoting component is injected in the form of gas (mist) from the injection well 14, and the moisture in the soil are collected by suction. In doing so
Even if the soil on the contaminated ground is in an unsaturated zone, the purification-promoting component injected in the purification-promoting-component injection process in the preceding process can be recovered together with gaseous substances as much as possible.
By collecting and reusing expensive decomposed microorganisms, ground purification costs can be reduced as much as possible. In addition,
The water separated by the gas-liquid separation device 32 is returned to the storage tank 24 by a return pipe 32a, and the decomposed microorganisms collected together with the water separated by the gas-liquid are returned to the storage tank.

【0038】ここで、図2に示すように当該実施形態の
浄化方法では、注入井14を掘削井13の多孔質管30
内で昇降自在となし、注入井14の噴出口14aからの
浄化促進成分の注入位置を上下方向に調整可能にしてあ
る。即ち、注入井14はその噴出口14aが多孔質管3
0の最深部に位置した状態で、その上端部が当該多孔質
管の上端部よりも上方に突出するようにし、この突出し
た上端部に高圧間欠注入装置16を取り付けている。そ
して、注入井14の外周には噴出口14aの上方に位置
してパッカー42を取り付け、該パッカー42を多孔質
管30の内周に摺動自在に密接させることにより、噴出
口14aから注入される浄化促進成分が上方に逃げるの
を防止して、集中して汚染地盤12中に吹き込めるよう
にしている。更に望ましくは、図示省略したが噴出口1
4aの下側に注入井14と一体となって昇降し、多孔質
管30内を摺動自在に密閉するパッカーを設けることに
より、注入される浄化促進成分の集中度を更に向上させ
得る。なお、多孔質管30は、周方向に複数のスリット
を管長方向に沿わせて上下延設した構成としても良く、
このようなスリット管も含むものである。
Here, as shown in FIG. 2, in the purification method of this embodiment, the injection well 14 is connected to the porous pipe 30 of the drilling well 13.
The injection position of the purification-promoting component from the injection port 14a of the injection well 14 can be adjusted in the vertical direction. In other words, the injection well 14 has its spout 14a
In the state located at the deepest part of the porous tube, its upper end protrudes above the upper end of the porous tube, and the high-pressure intermittent injection device 16 is attached to the protruded upper end. Then, a packer 42 is attached to the outer periphery of the injection well 14 above the jet port 14a, and the packer 42 is slidably brought into close contact with the inner circumference of the porous tube 30 to be injected from the jet port 14a. The purification promoting component is prevented from escaping upward, and can be concentrated and blown into the contaminated ground 12. More preferably, although not shown in the drawings, the ejection port 1
By providing a packer that moves up and down integrally with the injection well 14 and slidably seals the inside of the porous tube 30 below 4a, the concentration of the purification promoting component to be injected can be further improved. The porous pipe 30 may have a configuration in which a plurality of slits are vertically extended along a pipe length direction in a circumferential direction,
Such a slit tube is also included.

【0039】従って、この実施形態では注入井14を昇
降することにより噴出口14aを昇降できるため、1つ
の注入井14で浄化促進成分の注入位置を上下変化する
ことができる。このため、汚染地盤12の汚染領域の深
度が大きい場合にも浄化促進成分を上下方向に均等に吹
き込んで、地盤12の浄化を上下方向に均等化すること
ができる。従って、1基の注入井14での浄化領域が更
に拡大されるため、浄化装置10b全体で注入井14の
数を更に削減することができる。また、この実施形態で
は、吸引井30の位置を噴出口14aの位置によって変
化させることが望ましい。
Therefore, in this embodiment, the injection port 14a can be moved up and down by moving up and down the injection well 14, so that the injection position of the purification promoting component can be changed up and down in one injection well 14. Therefore, even when the depth of the contaminated area of the contaminated ground 12 is large, the purification promoting component is blown evenly in the vertical direction, so that the purification of the ground 12 can be equalized in the vertical direction. Therefore, since the purification area in one injection well 14 is further expanded, the number of injection wells 14 in the entire purification apparatus 10b can be further reduced. Further, in this embodiment, it is desirable to change the position of the suction well 30 depending on the position of the jet port 14a.

【0040】[0040]

【発明の効果】以上説明したように本発明の請求項1に
示す汚染地盤の浄化方法では、浄化促進成分注入工程に
ある掘削井には、浄化促進成分が超高圧(例えば2〜1
0気圧)をもって短時間の間隔でパルス状にされて間欠
的(例えば、1/30〜1/5HZの周期)に供給されるため、
該浄化促進成分は該掘削井から汚染地盤中に所定の間欠
タイミングをもって超高圧で爆発的に吹き込まれること
になる。このため、掘削井から汚染地盤中に注入される
浄化促進成分はより遠くかつより広い範囲に拡散して到
達されることになり、汚染地盤中の汚染物質を広範囲に
亘って浄化して、1基当たりの注入井での浄化領域を大
幅に拡大することが可能になる。また、浄化促進成分の
爆発的注入はパルス状にされて間欠的に継続して繰り返
されるため、注入の度に地盤の堆積状況に変化を及ぼし
て浄化促進成分の通り道がランダムになり易く、地盤全
体を可及的にほぼ均一に浄化可能となる。更に、混在す
る汚染物質等に適した浄化促進成分の注入を間欠注入で
実施することにより、注入成分の濃度の管理を容易にし
て無駄が無くなる。
As described above, according to the method for purifying contaminated ground according to the first aspect of the present invention, the excavation well in the step of injecting the purification promoting component has an ultrahigh pressure (for example, 2 to 1).
0 atm) and pulsed at short time intervals and intermittently supplied (eg 1/30 to 1 / 5HZ cycle),
The purification promoting component is explosively blown from the drilling well into the contaminated ground at an extremely high pressure at a predetermined intermittent timing. For this reason, the purification promoting component injected into the contaminated ground from the drilling well is diffused and reaches a farther and wider area, and the contaminants in the contaminated ground are purified over a wide area, and 1 It is possible to greatly expand the purification area per injection well. In addition, since the explosive injection of the purification-promoting component is intermittently repeated in the form of a pulse, the path of the purification-promoting component is likely to be random at each injection, and the path of the purification-promoting component is likely to be random. The whole can be purified as uniformly as possible. Further, by intermittently injecting a purification promoting component suitable for mixed contaminants and the like, the concentration of the injected component can be easily controlled and waste can be eliminated.

【0041】また、回収浄化処理工程にある掘削井から
は、土壌の浄化時に発生する分解ガスや、上記注入井か
ら浄化促進成分をガス(霧)状にして注入した際の余剰
ガス、および土壌中の水分等が吸引されるため、不飽和
帯の土壌であっても、その前工程の浄化促進成分注入工
程で注入した浄化促進成分をガス状物質とともに可及的
に回収できるようになり、特に、高価である分解微生物
を回収再利用することで、地盤浄化コストの可及的な低
減化が図れるようになる。
Further, from the drilling well in the recovery and purification treatment step, the decomposition gas generated at the time of soil purification, the surplus gas when the purification promoting component is injected in the form of gas (mist) from the injection well, and the soil Because the water and the like in the inside are sucked, even in the soil in the unsaturated zone, the purification promoting component injected in the purification promoting component injection process in the preceding process can be recovered as much as possible together with the gaseous substances, In particular, by collecting and reusing expensive decomposed microorganisms, the cost of ground purification can be reduced as much as possible.

【0042】加えて、浄化促進成分注入工程と回収浄化
処理工程とを切り替える場合に、隣接する工程の異なる
掘削井相互間で、注入井と吸引手段とを付け替えるだけ
で済み、工程移行が容易に行え、施工性に優れる。
In addition, when switching between the purification promoting component injection step and the recovery purification treatment step, it is only necessary to replace the injection well and the suction means between the drilling wells in different adjacent steps, and the process can be easily shifted. It can be performed and has excellent workability.

【0043】請求項2に示す浄化方法では、浄化促進成
分注入工程の掘削井から浄化促進成分を汚染地盤中に注
入する一方で、その周囲に隣接する回収浄化処理工程の
掘削井からガス状物質を吸引するので、浄化促進成分が
より拡散し易くなるとともに、分解ガスや余剰ガス等の
有害なガス状物質が地盤から自然に大気中に放出される
前に、これらを吸引井で捕集して浄化処理した後に放出
できるため、大気汚染を可及的に防止することができ
る。
According to the purification method of the present invention, while the purification promoting component is injected into the contaminated ground from the drilling well in the purification promoting component injection step, the gaseous substance is removed from the drilling well in the recovery and purification processing step adjacent thereto. As the purification promoting components are more easily diffused, harmful gaseous substances such as decomposition gas and surplus gas are collected by the suction well before they are naturally released from the ground to the atmosphere. Since it can be released after purification treatment, air pollution can be prevented as much as possible.

【0044】請求項3に示す浄化方法では、上記浄化促
進成分に、空気や過酸化水素やオゾン等の酸素含有物
質、分解微生物、分解微生物を活性化する栄養源、など
の汚染物質の浄化を促進する成分を用いることにより、
各種汚染物質に即した浄化を適正に行うことができる。
In the purification method according to the third aspect, the purification-promoting component is used to purify contaminants such as oxygen-containing substances such as air, hydrogen peroxide and ozone, decomposing microorganisms, and nutrient sources for activating the decomposing microorganisms. By using a promoting component,
Purification suitable for various pollutants can be performed properly.

【0045】請求項4に示す浄化方法では、上記掘削井
の内周には多孔質管を配置して、前記浄化促進成分注入
工程では、該多孔質管内部に、先端に噴出口を有すると
ともに該噴出口の上側に該多孔質管に密接してシールす
るパッカーが取り付けられた注入井を挿入して、該噴出
口から前記浄化促進成分を間欠供給する一方、前記回収
浄化処理工程では、該多孔質管の上端部に吸引手段を接
続してガス状物質を吸引回収するので、1つの掘削井で
の浄化促進成分の注入位置を上下に変化させて調整する
ことができ、汚染地盤の汚染領域の深度が大きい場合に
も浄化促進成分を上下方向に均等に吹き込んで、地盤の
浄化を上下方向に均等化することができる。また、浄化
促進成分注入工程と回収浄化処理工程との工程移行を行
う際に、注入井と吸引手段を備えた回収浄化処理設備と
の付け替え作業が簡易に行え、工程移行の作業性に優れ
る。
According to a fourth aspect of the present invention, a porous pipe is disposed on the inner periphery of the drilling well, and in the step of injecting the purification promoting component, the porous pipe has a spout at a tip thereof. An injection well equipped with a packer that seals closely to the porous tube is inserted above the jet port to intermittently supply the purification accelerating component from the jet port. The suction means is connected to the upper end of the porous pipe to suction and collect gaseous substances. Therefore, the injection position of the purification promoting component in one drilling well can be adjusted by changing the position up and down, thereby contaminating the contaminated ground. Even when the depth of the region is large, the purification promoting component is evenly blown in the vertical direction, so that the purification of the ground can be equalized in the vertical direction. Further, when performing the process transition between the purification promoting component injecting step and the recovery and purification processing step, the work of replacing the recovery and purification processing equipment with the injection well and the suction means can be easily performed, and the workability in the process transition is excellent.

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

【図1】本発明の一実施形態を概略的に示す断面図であ
る。
FIG. 1 is a sectional view schematically showing an embodiment of the present invention.

【図2】本発明の一実施形態の要部を概略的に示す断面
図であり、同図(a),(b)は浄化促進成分注入工程と
回収浄化処理工程との工程移行の前後の状態を示すもの
である。
FIGS. 2A and 2B are cross-sectional views schematically showing a main part of one embodiment of the present invention, wherein FIGS. 2A and 2B show before and after the process transition between a purification promoting component injection step and a recovery purification treatment step. It shows the status.

【符号の説明】[Explanation of symbols]

10 浄化装置 12 汚染地盤 13 掘削井 14 注入井 14a 噴出口 16 高圧間欠注入装置 18 供給経路 20 浄化促進成分供給設備 30 多孔質管 31 吸引井 32 気液分離器 34 吸引ポンプ 36 排出ガス浄化装置 38 浄化ガス排気設備 40 回収浄化処理設備 42 パッカー DESCRIPTION OF SYMBOLS 10 Purification apparatus 12 Contaminated ground 13 Drilling well 14 Injection well 14a Spout port 16 High-pressure intermittent injection apparatus 18 Supply path 20 Purification promoting component supply equipment 30 Porous pipe 31 Suction well 32 Gas-liquid separator 34 Suction pump 36 Exhaust gas purification apparatus 38 Purified gas exhaust equipment 40 Recovery and purification processing equipment 42 Packer

───────────────────────────────────────────────────── フロントページの続き (72)発明者 辻 博和 東京都清瀬市下清戸4丁目640番地 株式 会社大林組技術研究所内 Fターム(参考) 2E191 BA11 BB01 BC01 BC05 BD11 BD20 4D004 AA41 AC07 CA18 CA36 CC01 CC02 CC07 CC15  ──────────────────────────────────────────────────の Continuing on the front page (72) Inventor Hirokazu Tsuji 4-640 Shimoseito, Kiyose-shi, Tokyo F-term in Obayashi Corporation Technical Research Institute Co., Ltd. (Reference) 2E191 BA11 BB01 BC01 BC05 BD11 BD20 4D004 AA41 AC07 CA18 CA36 CC01 CC02 CC07 CC15

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 汚染地盤に削孔した掘削井に超高圧をも
って浄化促進成分を短時間の間隔でパルス状にして間欠
的に供給し、この掘削井からその周囲の汚染地盤中に浄
化促進成分を吹き込む浄化促進成分注入工程と、 該掘削井から地盤中のガス状物質を吸引回収し、この回
収したガス状物質を浄化処理により無害化して排出する
回収浄化処理工程とを有し、 該浄化促進成分注入工程と該回収浄化処理工程とを交互
に繰り返すことを特徴とする汚染地盤の浄化方法。
1. A purification promoting component is intermittently supplied to a drilling well drilled in a contaminated ground at an ultra-high pressure in the form of pulses at short intervals and intermittently supplied from the drilling well into the surrounding contaminated ground. A purifying accelerating component injecting step, and a collecting and purifying step of sucking and collecting gaseous substances in the ground from the drilling well, detoxifying and discharging the collected gaseous substances by a purifying treatment, and A method for purifying contaminated ground, characterized by alternately repeating the accelerating component injection step and the recovery / purification processing step.
【請求項2】 前記掘削井を複数設け、浄化促進成分注
入工程にある掘削井に隣接する掘削井は回収処理工程と
なすことを特徴とする請求項1記載の汚染地盤の浄化方
法。
2. The method for purifying contaminated ground according to claim 1, wherein a plurality of the drilling wells are provided, and a drilling well adjacent to the drilling well in the purification promoting component injection step is a recovery processing step.
【請求項3】 上記浄化促進成分は、空気や過酸化水素
やオゾン等の酸素含有物質、分解微生物、分解微生物を
活性化する栄養源、などの汚染物質の浄化を促進する成
分であることを特徴とする請求項1または2のいずれか
に記載の汚染地盤の浄化方法。
3. The purification-promoting component is a component that promotes the purification of contaminants such as oxygen-containing substances such as air, hydrogen peroxide and ozone, decomposing microorganisms, and nutrient sources for activating decomposing microorganisms. The method for purifying contaminated ground according to claim 1, wherein:
【請求項4】 上記掘削井の内周に多孔質管を配置し、
前記浄化促進成分注入工程では、該多孔質管内部に、先
端に噴出口を有するとともに該噴出口の上側に該多孔質
管に密接してシールするパッカーが取り付けられた注入
井を挿入して、該噴出口から前記浄化促進成分を間欠供
給する一方、前記回収浄化処理工程では、該多孔質管の
上端部に吸引手段を備えた回収浄化処理設備を接続して
ガス状物質を吸引回収することを特徴とする請求項1〜
3のいずれかに記載の汚染地盤の浄化方法。
4. A porous pipe is arranged on an inner periphery of the drilling well,
In the purification promoting component injection step, an injection well having a spout at the tip and having a packer tightly sealed to the porous pipe is inserted above the spout inside the porous tube, While intermittently supplying the purification-promoting component from the jet port, in the recovery-purification processing step, a suction-recovery processing facility equipped with a suction means is connected to the upper end of the porous tube to suction-recover gaseous substances. Claims 1 to
3. The method for purifying contaminated ground according to any one of 3.
JP31538099A 1999-11-05 1999-11-05 Purification method for contaminated ground Expired - Fee Related JP3646589B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006198566A (en) * 2005-01-24 2006-08-03 Shimane Pref Gov High-pressure air supply device for promotion of aerobic fermentation and fermentation method
WO2008037069A1 (en) * 2006-09-25 2008-04-03 Wavefront Reservoir Technologies Ltd. Placement of fluids in ground by pulse-injection
JP2012061431A (en) * 2010-09-16 2012-03-29 Panasonic Corp Apparatus and method for cleaning ground water
KR101443883B1 (en) * 2014-03-07 2014-09-23 한국지질자원연구원 Remediation of soil contaminated with petroleum in oil-sand area
JP6031705B2 (en) * 2011-05-16 2016-11-30 学校法人福岡大学 Environmental restoration device and environmental restoration method
CN112028222A (en) * 2020-07-13 2020-12-04 安徽国祯环境修复股份有限公司 Underground water repairing system and method thereof

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006198566A (en) * 2005-01-24 2006-08-03 Shimane Pref Gov High-pressure air supply device for promotion of aerobic fermentation and fermentation method
WO2008037069A1 (en) * 2006-09-25 2008-04-03 Wavefront Reservoir Technologies Ltd. Placement of fluids in ground by pulse-injection
EP2074280A1 (en) * 2006-09-25 2009-07-01 Wavefront Reservoir Technologies Ltd. Placement of fluids in ground by pulse-injection
US8166992B2 (en) 2006-09-25 2012-05-01 Wavefront Reservoir Technologies Ltd. Placement of fluids in ground by pulse-injection
EP2074280A4 (en) * 2006-09-25 2015-06-24 Wavefront Reservoir Technologies Ltd Placement of fluids in ground by pulse-injection
JP2012061431A (en) * 2010-09-16 2012-03-29 Panasonic Corp Apparatus and method for cleaning ground water
JP6031705B2 (en) * 2011-05-16 2016-11-30 学校法人福岡大学 Environmental restoration device and environmental restoration method
KR101443883B1 (en) * 2014-03-07 2014-09-23 한국지질자원연구원 Remediation of soil contaminated with petroleum in oil-sand area
CN112028222A (en) * 2020-07-13 2020-12-04 安徽国祯环境修复股份有限公司 Underground water repairing system and method thereof

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