JP2002273403A - Purification method of contaminated soil - Google Patents

Purification method of contaminated soil

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Publication number
JP2002273403A
JP2002273403A JP2001075733A JP2001075733A JP2002273403A JP 2002273403 A JP2002273403 A JP 2002273403A JP 2001075733 A JP2001075733 A JP 2001075733A JP 2001075733 A JP2001075733 A JP 2001075733A JP 2002273403 A JP2002273403 A JP 2002273403A
Authority
JP
Japan
Prior art keywords
contaminated soil
iron powder
contaminated
purification
construction
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2001075733A
Other languages
Japanese (ja)
Inventor
Takashi Yamamoto
貴士 山本
Nobuo Hamamoto
信雄 濱本
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.)
ECO-SYSTEM ENGINEERING CO Ltd
Seiko Kogyo Co Ltd
Original Assignee
ECO-SYSTEM ENGINEERING CO Ltd
Seiko Kogyo Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by ECO-SYSTEM ENGINEERING CO Ltd, Seiko Kogyo Co Ltd filed Critical ECO-SYSTEM ENGINEERING CO Ltd
Priority to JP2001075733A priority Critical patent/JP2002273403A/en
Publication of JP2002273403A publication Critical patent/JP2002273403A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To provide a purification method in which only a part in which contaminated soil exists is selected, the region of execution of purification works is specified either in the planar direction or in the depth direction and an iron powder is mixed only into the contaminated soil of a necessary part. SOLUTION: In this purification method, the soil contaminated with an organic chlorine-based compound is purified by mixing the contaminated soil and the iron powder with the use of an auger 1, a specified contaminated underground soil layer is made to be the object of purification, a space between the ground surface of the region of purification object and the layer of contaminated ground is dug while ejecting air from a digging drill, subsequently, the whole region of contaminated soil layer is dug likewise while ejecting the iron powder from the digging drill 4, thereafter, the mixed soil of the contaminated soil and the iron powder is confined in the original position by pulling out a digging shaft while reversing the same and the contaminated soil is thus made harmless.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、有機塩素系化合物によ
り汚染された土壌の鉄粉による浄化技術に関し、特に、
汚染された土壌の深度方向でその汚染度にバラツキがあ
る原位置において、浄化が必要である土壌層のみを作業
効率良く経済的に浄化できる汚染土壌の浄化工法に関す
るものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a technique for purifying soil contaminated with organochlorine compounds using iron powder.
The present invention relates to a method for purifying contaminated soil that can economically purify only a soil layer that needs to be purified at an original position where the degree of contamination varies in the depth direction of the contaminated soil with high working efficiency.

【0002】[0002]

【従来の技術】半導体工場や金属加工工場の跡地等にお
ける、有機塩素系化合物による汚染土壌の浄化に鉄粉を
利用する技術は、例えば特開平11−235577号公
報等において既に提案されている。該公報に係る土壌の
無害化処理方法は、ジクロロメタン、四塩化炭素、1,
2−ジクロロエタン、1,1,1−トリクロロエタン、
1,1,2−トリクロロエタン、トリクロロエチレン、
テトラクロロエチレン、1,3−ジクロロプロペン等の
揮発性有機塩素系化合物やPCB、ダイオキシン類等の
有機塩素系化合物により汚染された土壌を浄化する場合
に、鉄粉を用いてこれらの有機塩素系化合物を脱塩素あ
るいは脱塩化水素作用により、分解させ無害化するもの
である。
2. Description of the Related Art A technique of using iron powder for purifying soil contaminated with an organic chlorine compound at a site of a semiconductor factory or a metal processing factory has already been proposed in, for example, Japanese Patent Application Laid-Open No. 11-235577. The method for detoxifying soil according to the publication includes dichloromethane, carbon tetrachloride, 1,
2-dichloroethane, 1,1,1-trichloroethane,
1,1,2-trichloroethane, trichloroethylene,
When purifying soil contaminated with volatile organic chlorine-based compounds such as tetrachloroethylene and 1,3-dichloropropene and PCBs and organic chlorine-based compounds such as dioxins, these organic chlorine-based compounds are removed using iron powder. It is decomposed and made harmless by the action of dechlorination or dehydrochlorination.

【0003】そして、原位置処理の場合には、空気又は
水等による高圧媒体を利用して地中に鉄粉を散布する方
法、地盤改良工事で利用される土木機械を用いて、土壌
に鉄粉を機械的に掘削混合する方法等が示唆されてい
る。また、汚染土壌に対する鉄粉の混合割合を0.1重
量%〜10重量%の範囲で、浄化すべき全土壌と混合す
ることも示唆されている。
[0003] In the case of in-situ treatment, a method of spraying iron powder into the ground by using a high-pressure medium such as air or water, and a method of using a civil engineering machine used for ground improvement work to add iron to soil. A method of mechanically excavating and mixing the powder has been suggested. It is also suggested that iron powder be mixed with all soil to be purified in a mixing ratio of iron powder to contaminated soil in a range of 0.1% by weight to 10% by weight.

【0004】ところで、例えば上記半導体工場や金属加
工工場のような有機塩素系化合物による汚染地にあって
も、土壌の成分によってその深さ方向の位置における汚
染度合は大きく異なるものである。詳細には、汚染地盤
の上層部が砂礫等の土質の場合、地表に漏れ出た汚染物
質である塩素系化合物が雨水等により地中に流下され、
年月の経過と共に砂礫層の汚染は自然に浄化されている
場合が多い。
By the way, even in a contaminated area such as the above-mentioned semiconductor factory or metal processing factory, the degree of contamination at a position in the depth direction greatly varies depending on the components of the soil. In detail, when the upper part of the contaminated ground is soil such as sand and gravel, chlorine-based compounds, which are pollutants leaking to the surface of the ground, flow down into the ground due to rainwater, etc.
Over time, the gravel layer has often been naturally purified.

【0005】その反面、地層中にシルト層やシルト混合
層等が存在すると、その汚染度合が増大し、極めて高い
濃度の汚染帯が存在することがボーリング調査で明らか
になった。また、このような汚染帯は地下水域で特に顕
著であり、雨水により流下された汚染物質はこの様な地
下水域に滞留するものと考えられる。
On the other hand, when a silt layer or a silt mixed layer is present in the formation, the degree of contamination increases, and it has been found by boring surveys that a very high concentration of contamination zone exists. Further, such a polluted zone is particularly remarkable in a groundwater area, and it is considered that pollutants that have flowed down by rainwater stay in such a groundwater area.

【0006】更に、実際の汚染源から可成り離れた地域
においても、その地下の一定深度部分が高濃度で汚染さ
れている場合もある。この様な場合は、上記のごとき汚
染地において雨水等により流下された汚染物質が地下水
により拡散又は移動され、特にその地下水の下流側と見
られる方向に汚染物質をより多く拡散したものと考えら
れるが、このような場所にあっては、現実の汚染土壌は
地下の一定深度の特に地下水帯域のみであって、その上
方における部分はあまり汚染されていないものである。
[0006] Furthermore, even in an area far away from the actual source of contamination, a certain depth under the ground may be highly contaminated. In such a case, it is considered that the contaminant that has flowed down by rainwater or the like in the contaminated area as described above was diffused or moved by the groundwater, and in particular, the contaminant was more diffused in a direction viewed as the downstream side of the groundwater. However, in such a place, the actual contaminated soil is only the groundwater zone at a certain depth below the ground, and the portion above it is not much contaminated.

【0007】[0007]

【発明が解決しようとする課題】上記汚染地域又は汚染
地層の現状に鑑み、本発明は現実に汚染土壌が存在する
部分のみを選択し、確実にかつ迅速に浄化処理できる鉄
粉による汚染土壌の浄化工法を提供するものであって、
特に、浄化工事の施工域を平面方向にも深度方向にも特
定し、必要な部位の汚染土壌にのみ鉄粉を混合する、よ
り経済的で効率の良い浄化工法を提供するものである。
SUMMARY OF THE INVENTION In view of the present situation of the above-mentioned contaminated area or contaminated stratum, the present invention selects only a portion where contaminated soil actually exists, and can reliably and quickly purify the contaminated soil with iron powder. Providing a purification method,
In particular, it is intended to provide a more economical and efficient purification method in which the construction area of the purification work is specified both in the horizontal direction and in the depth direction, and iron powder is mixed only in the contaminated soil at a necessary portion.

【0008】[0008]

【課題を解決するための手段】本発明は、有機塩素系化
合物によって汚染された土壌を、その汚染土壌と鉄粉と
をオーガを使用して混合することにより浄化する工法で
あって、地下の特定汚染土壌層を対象とし、浄化対象域
の地表から汚染地層までの間をオーガの掘削ドリルから
空気を吐出しながら掘削し、続いて汚染土壌層全域を同
様に掘削ドリルから鉄粉を吐出しながら掘削し、その後
掘削軸を逆転しながら引き抜くことによって汚染土壌と
鉄粉との混合土を元位置に封じ込めて汚染物質の無害化
を行うことを特徴とする浄化工法である。またこのよう
な浄化工法において、汚染土壌層全域を掘削ドリルから
鉄粉を吐出しながら掘削した後に、掘削軸を回転させな
がら上下動することによって、汚染土壌と鉄粉とを更に
撹拌することもできる。本発明の浄化工法は更に、オー
ガにより汚染土壌層に鉄粉を吐出混合するための掘削
を、施工地表面で見て施工域の列と非施工域帯とを交互
に繰り返し、該列相互の間隔を約2m〜5m離間させて
施工し、又は、施工地面で見て各一回毎の施工域の相互
の間隔を、夫々約2m〜5m離間させて施工することに
より浄化地盤の耐力を保持することを特徴としている。
そして、本発明の浄化工法は土壌汚染の度合に応じて又
は浄化地層の水分の量に応じて、混合する鉄粉の量を可
変とすることを特徴としている。
SUMMARY OF THE INVENTION The present invention relates to a method for purifying soil contaminated with an organochlorine compound by mixing the contaminated soil with iron powder using an auger. Drilling is performed for the specified contaminated soil layer from the surface of the area to be purified to the contaminated layer while discharging air from the auger drilling drill, and then the entire area of the contaminated soil layer is similarly discharged with iron powder from the drilling drill. This is a purification method characterized in that contaminated soil and a mixture of iron powder are confined in the original position by excavating while excavating and then pulling out while reversing the excavation axis to detoxify contaminants. Further, in such a purification method, after excavating the entire contaminated soil layer while discharging iron powder from a drill, the contaminated soil and the iron powder may be further stirred by rotating up and down the drilling axis. it can. Further, the purification method of the present invention further includes excavation for discharging and mixing the iron powder into the contaminated soil layer by the auger, and alternately repeats the rows of the construction area and the non-construction area when viewed on the construction ground surface. Maintain the strength of the purification ground by constructing with an interval of about 2m to 5m apart, or by constructing with a mutual interval of about 2m to 5m each in the construction area each time viewed from the construction ground. It is characterized by doing.
The purification method of the present invention is characterized in that the amount of iron powder to be mixed is made variable according to the degree of soil contamination or the amount of water in the purification layer.

【0009】[0009]

【発明の実施の形態】本発明の実施の形態を図1〜図6
によって説明する。図1は、通常の単軸式アースオーガ
又は三軸式アースオーガ1を用い、その掘削軸芯を施工
杭芯にセットする状態を示している。この場合に、例え
ば三軸式アースオーガ1の掘削軸2は、回転駆動装置3
により回動しながら掘削し、その先端のドリル4から必
要な時期に、汚染土壌浄化のための鉄粉を必要量吐出す
ることができるものである。この様なアースオーガ1
は、上記ドリル4の端部から空気や水等を適宜に吐出し
ながら掘削可能な形式のものである。
1 to 6 show an embodiment of the present invention.
It will be explained by. FIG. 1 shows a state in which a normal single-axis earth auger or a three-axis earth auger 1 is used, and the excavation axis is set on a construction pile core. In this case, for example, the excavating shaft 2 of the triaxial earth auger 1
In this way, a required amount of iron powder for purifying contaminated soil can be discharged from the drill 4 at the tip thereof at a required time. Earth Auger 1
Is of a type capable of excavating while appropriately discharging air or water from the end of the drill 4.

【0010】図2はアースオーガ1によって、浄化すべ
き土壌の上端部までの距離、すなわち非汚染土壌層L
を掘削した状態を示しており、通常この位置までの掘削
はドリル4の端部から空気を噴出させながら行なわれ
る。この場合、例えば地下水により地層の下部である地
下水層以下が汚染されているような場所において、その
汚染土壌層のみに鉄粉を混合するため、その浄化施工位
置までは通常の掘削が行なわれる。
FIG. 2 shows the distance to the top end of the soil to be purified by the earth auger 1, that is, the non-contaminated soil layer L 1.
Is drilled, and the drilling up to this position is usually performed while blowing air from the end of the drill 4. In this case, for example, in a place where the groundwater below the groundwater layer is contaminated by the groundwater, since the iron powder is mixed only with the contaminated soil layer, ordinary excavation is performed up to the purification work position.

【0011】図3は、実際に浄化されるべき汚染土壌層
の削孔状態を示している。図2に示す通常削孔によ
り、掘削ドリル4の端部から空気を吐出しながら非汚染
土壌層であるL部分を削孔し、続いて上記吐出空気に
鉄粉を注入しながら、更に汚染土壌層に相当するL
深度を掘進する。この場合の掘削軸2の掘進速度は、例
えば10〜30cmピッチで、毎分50cm程度の速度
で削孔を行うものである。
[0011] Figure 3 shows a drilling state of the contaminated soil layer L 2 to be actually clean. By conventional drilling shown in FIG. 2, and drilling the L 1 moiety is a non-contaminated soil layer while discharging air from the end of drilling the drill 4, followed with injection of iron powder to the discharge air, further pollution the excavation depth of L 2, which corresponds to the soil layer. In this case, the excavating speed of the excavating shaft 2 is, for example, a pitch of 10 to 30 cm, and drills holes at a speed of about 50 cm per minute.

【0012】図4は、一応図3の状態において浄化が必
要な汚染土壌中に必要量の鉄粉の注入を終了した後、必
要に応じて反復撹拌を行う工程を示している。この様な
撹拌工程は、例えば掘削軸2を回動しながら約3m上下
動させるだけで、鉄粉の注入深度Lに渡って全域に掘
削ドリル4部分を移動させる必要はない。
FIG. 4 shows a process of repeating the stirring as necessary after the injection of the required amount of iron powder into the contaminated soil which needs to be purified in the state of FIG. Such agitation step, for example by drilling shaft 2 only by about 3m vertical movement while rotating, it is not necessary to move the excavation drill 4 portions over the entire area over the implanted depth L 2 of the iron powder.

【0013】図5は、浄化のための鉄粉注入及び撹拌混
合終了後に、アースオーガ1の掘削軸2を引き上げた状
態を示しており、該引き上げ工程においては掘削軸2を
逆転しながら引き上げるものである。これは、鉄粉が混
合された汚染土壌の非汚染部分への拡散を防止すること
にも役立つものである。この様にして同図の浄化必要部
分土壌層である、地表から深度Lだけ下がった位置か
ら施工深度Lに渡って、鉄粉混合域5が施工される。
FIG. 5 shows a state in which the excavating shaft 2 of the earth auger 1 is pulled up after the injection of the iron powder for purification and the mixing and stirring are completed. It is. This also helps to prevent the spread of contaminated soil mixed with iron powder to non-contaminated parts. A cleaning necessary part soil layer in the same figure. In this way, over from the position lowered by the depth L 1 from the surface to the construction depth L 2, iron powder mixing zone 5 is construction.

【0014】図6は、三軸式アースオーガを用いて実際
に鉄粉の混合を行う施工域Hの平面的施工域分布と、
その掘削作業を行う手順の種々の態様を示している。図
6(A)においては、いわゆるセミラップ方式によって
,H,H,H……の順に夫々掘削を行い、先
ず第1の列Lを施工する。この場合の掘削施工は当然
に上記図1〜図5の手順に沿って行い、鉄粉の吐出混合
は浄化必要土壌層のみである。次に該第1の列Lから
αの距離を隔てた位置に第2の列Lを、HからH
n+1、Hn+2……の順で第1の列と同様にして、上記
掘削及び鉄粉の吐出混合を繰り返し施工するものであ
る。
FIG. 6 shows an example using a triaxial earth auger.
Area H for mixing iron powdernAnd the flat construction area distribution of
Various aspects of the procedure for performing the excavation work are shown. Figure
In 6 (A), the so-called semi-wrap method
H1, H2, H3, H4Excavate in the order of ……
First row L1To construct. Excavation in this case is natural
And the discharge mixing of the iron powder
Is only the soil layer that needs purification. Next, the first column L1From
a second row L at a position separated by a distance of α2And HnTo H
n + 1, Hn + 2In the same manner as in the first column in the order of
Excavation and discharge mixing of iron powder are performed repeatedly.
You.

【0015】この場合に、第1の列Lにおいて、例え
ばHとHとの各施工域は互いに一部重複している
が、その重複部分の面積は僅かであり、一回の掘削混合
工程によって略三軸の掘削軸巾分だけ浄化作業が進行す
ることとなる。そして、第2の列Lの施工にあたって
は、図示のごとく第1の列Lと距離αだけ隔てて施工
されるので、この非施工域である距離αに対応する地盤
の汚染層における土壌の浄化は、上記施工域又は施工域
の列において浄化必要部分に混合された鉄粉によって行
われることとなる。
[0015] In this case, in the first row L 1, for example, the construction area of the H 1 and H 2 are partially overlapping each other, the area of the overlapping portion is small, a single drilling By the mixing process, the cleaning operation proceeds by the width of the substantially three-axis excavation shaft. And, when the construction of the second column L 2, since it is construction apart by a first row L 1 and the distance α as shown in the drawing, the soil in the contaminated layer of the ground corresponding to the distance α is the non-construction zone Purification is performed by the iron powder mixed in the required area for purification in the construction area or the row of the construction area.

【0016】図6(B)に示す施工手順は、完全ラップ
方式により上記第1、第2に相当する列L,Lを施
工する状態を示している。この場合には、各回の掘削工
程において三軸の両側の2本の掘削軸は結果的に相互に
重複して施工されることとなり、施工速度は可成り低下
するけれども、掘削方向(垂直方向)の施工精度が格段
に向上するので、非施工域における地盤耐力の保持がよ
り確実に行われる利点がある。
The construction procedure shown in FIG. 6 (B) shows a state where the rows L 1 and L 2 corresponding to the first and second rows are constructed by the complete wrapping method. In this case, in each excavation process, the two excavation axes on both sides of the three axes are consequently overlapped with each other, and the construction speed is considerably reduced, but the excavation direction (vertical direction) The construction accuracy is greatly improved, and there is an advantage that the ground strength in the non-construction area is more reliably maintained.

【0017】図6(C)に示す施工手順はいわゆる単独
方式によるものであって、各施工域H〜Hは相互に
距離αだけ隔たっている。そして、上記と同様に非施工
域の汚染層における土壌汚染は施工域内の汚染土壌に混
合された鉄粉により浄化されることとなるが、極めて高
い施工速度を得ることができるものである。また、混合
される鉄粉の量は一定の範囲で増減できるので、非施工
域内の土壌の汚染物質も施工域内において混合された鉄
粉によって充分に分解無害化することができる。
The construction procedure shown in FIG. 6C is based on a so-called single system, and the construction areas H 1 to H n are separated from each other by a distance α. Then, similarly to the above, soil contamination in the contaminated layer in the non-construction area is purified by iron powder mixed with the contaminated soil in the construction area, but an extremely high construction speed can be obtained. Further, since the amount of iron powder mixed can be increased or decreased within a certain range, soil contaminants in the non-construction area can be sufficiently decomposed and made harmless by the iron powder mixed in the construction area.

【0018】[0018]

【実施例】上記汚染土壌層に対応した鉄粉の吐出混合域
の実験例を示すと次のようである。この実験例にあって
は、試験的浄化工事地域がいわゆる火山地帯であったた
めに、汚染土壌層が深く、また、深度方向の地質と汚染
層との関係は次のごとくであった。ボーリング調査によ
り、深度64mまでの土質と採集土壌の汚染度を測定し
た。その結果、地表から約14mまでは砂礫層と礫混じ
り砂層が互層を呈しており、その間はほとんど汚染され
ていない。深度15m〜52m附近までの地層は、その
間に約0.8m〜1.0mのシルト質又は粘土混じりシ
ルト層を三ヶ所挟んで、非溶結凝灰岩又は凝灰質砂層が
互層を成しており、深度約52m以下は地下水層を形成
している。そして、該地下水層に対応する深度52m〜
64mにおいては、凝灰質砂、中溶結凝灰岩、火山灰質
砂、礫混じり粘土等の地層が繰り返されている。
EXAMPLE An experimental example of an iron powder discharge mixing area corresponding to the above-mentioned contaminated soil layer is as follows. In this experimental example, since the experimental purification area was a so-called volcanic zone, the contaminated soil layer was deep, and the relationship between the geology in the depth direction and the contaminated layer was as follows. By boring survey, the soil quality up to a depth of 64 m and the pollution degree of the collected soil were measured. As a result, up to about 14 m from the surface of the ground, the gravel layer and the gravel-mixed sand layer are in alternating layers, with little contamination between them. The stratum from 15m to 52m depth has three layers of silt or silt mixed with clay of about 0.8m to 1.0m in between. About 52 m or less forms a groundwater layer. The depth corresponding to the groundwater layer is 52 m or more.
At 64 m, strata such as tuff sand, medium welded tuff, volcanic ash sand, and clay mixed with gravel are repeated.

【0019】これに対して土壌汚染状況は、深度約16
mから急激に汚染が進行しており、更に深度約53mか
ら約63mまでは特に汚染度が著しく、また、深度約6
3〜64mは特に汚染されていないと判明した。そこ
で、今回の試験的浄化工事にあたっては、深度約13m
までを上記図2に示す工程により掘削し、深度約13m
から深度約52mまでは図3に示す工程を施工し、この
間の鉄粉吐出量を、単位掘削土壌1m当り20kg注
入することとし、深さ約52mから同64mまでを同じ
く図3に示す工程により掘削し、その間の鉄粉吐出量を
単位掘削土壌1m当り200kgとすることに決定し
た。また、三軸式アースオーガを使用し、図6(C)の
施工手順に従い、α=3mの施工間隔とすることに決定
した。
On the other hand, the soil contamination status is about 16
m, the pollution is rapidly progressing, and the degree of contamination is particularly remarkable from a depth of about 53 m to about 63 m.
3-64 m proved not to be particularly contaminated. Therefore, at the time of this trial purification work, about 13m depth
Up to the depth of about 13m
From to a depth of about 52m is applying a process shown in FIG. 3, during this period of iron powder discharge amount, and that the unit excavated soil 1 m 3 per 20kg injection, also up to the 64m from a depth of about 52m step shown in FIG. 3 excavated by, it was decided to iron powder discharge amount during a unit excavating the soil 1 m 3 per 200 kg. In addition, using a triaxial earth auger, and according to the construction procedure of FIG. 6 (C), it was determined that the construction interval was α = 3 m.

【0020】[0020]

【発明の効果】本発明によれば、施工現場の状況によっ
て地下の汚染層深度が異なる場合に、その汚染土壌層の
みに対して浄化施工が可能であり、しかも、汚染濃度又
は土壌環境に応じて最適な浄化工事が可能となり、極め
て経済的で迅速な浄化工事を行なうことができる。ま
た、非掘削域を設けることによって、浄化工事終了直後
より他の種々の作業を、浄化施工域地表面においても可
能とすることができる作用効果を奏するものである。
According to the present invention, when the depth of the underground contaminated layer differs depending on the construction site conditions, purification work can be performed only on the contaminated soil layer, and furthermore, according to the contamination concentration or soil environment. As a result, an optimum purification work can be performed, and an extremely economical and quick purification work can be performed. In addition, by providing the non-excavation area, there is an effect that various other works can be performed on the ground surface of the purification work area immediately after the completion of the purification work.

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

【図1】浄化施工時のオーガの掘削軸芯セット状態を示
す説明図である。
FIG. 1 is an explanatory view showing a state in which an auger excavation axis is set at the time of purification work.

【図2】非汚染土壌層Lの掘削状況説明図である。Figure 2 is a drilling situation illustration of uncontaminated soil layer L 1.

【図3】汚染土壌層Lの掘削状況説明図である。3 is a drilling situation illustration of contaminated soil layer L 2.

【図4】撹拌工程の説明図である。FIG. 4 is an explanatory view of a stirring step.

【図5】浄化掘削終了状況の説明図である。FIG. 5 is an explanatory diagram of a purification excavation end situation.

【図6】掘削施工域の平面的分布例を示す説明図であ
る。
FIG. 6 is an explanatory diagram showing a planar distribution example of an excavation work area.

【符号の説明】[Explanation of symbols]

1 アースオーガ 2 掘削軸 4 掘削ドリル L 非汚染土壌層 L 汚染土壌層 H 浄化施工域Reference Signs List 1 earth auger 2 drill axis 4 drill drill L 1 non-contaminated soil layer L 2 contaminated soil layer H n purification work area

フロントページの続き (72)発明者 濱本 信雄 東京都千代田区岩本町3−1−2 成幸工 業株式会社東京支店内 Fターム(参考) 4D004 AA41 AB06 CA34 CA45 CA47 CB24 CC11 Continued on the front page (72) Inventor Nobuo Hamamoto 3-1-2 Iwamotocho, Chiyoda-ku, Tokyo F-term (reference) in the Tokyo branch of Seiko Kogyo Co., Ltd. 4D004 AA41 AB06 CA34 CA45 CA47 CB24 CC11

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 有機塩素系化合物によって汚染された土
壌を、その汚染土壌と鉄粉とをオーガを使用して混合す
ることにより浄化する工法であって、地下の特定汚染土
壌層を対象とし、浄化対象域の地表から汚染地層までの
間をオーガの掘削ドリルから空気を吐出しながら掘削
し、続いて汚染土壌層全深さを同様に掘削ドリルから鉄
粉を吐出しながら掘削し、その後掘削軸を逆転しながら
引き抜くことによって掘削汚染土壌と鉄粉との混合土を
元位置に封じ込めて汚染物質の無害化を行うことを特徴
とする浄化工法。
1. A method of purifying soil contaminated with an organochlorine compound by mixing the contaminated soil and iron powder using an auger, and targeting a specific underground contaminated soil layer, Drilling is performed from the surface of the area to be cleaned to the contaminated layer while discharging air from the auger drill, and then the entire depth of the contaminated soil layer is also drilled while discharging iron powder from the drill and then drilling. A purification method characterized in that by removing the shaft while reversing the shaft, the mixed soil of excavated contaminated soil and iron powder is sealed in its original position to detoxify the pollutants.
【請求項2】 請求項1の浄化工法において、汚染土壌
層全深さを掘削ドリルから鉄粉を吐出しながら掘削した
後に、掘削軸を回転させながら上下動することによっ
て、掘削汚染土壌と鉄粉とを更に撹拌する工程を採用す
ることを特徴とする浄化工法。
2. The method according to claim 1, wherein after excavating the entire depth of the contaminated soil layer while discharging iron powder from the excavation drill, the excavated contaminated soil and the iron are moved up and down while rotating the excavation shaft. A purification method characterized by employing a step of further stirring the powder.
【請求項3】 上記オーガにより汚染土壌層に鉄粉を吐
出混合するための掘削は、施工地表面で見て施工域の列
と非施工域帯とを交互に繰り返し、該施工域の列相互の
間隔を約2m〜5m離間させて施工し、浄化地盤の耐力
を保持することを特徴とする請求項1又は2記載の浄化
工法。
3. The excavation for discharging and mixing the iron powder into the contaminated soil layer by the auger is performed by alternately repeating the rows of the construction area and the non-construction zone when viewed on the construction ground surface. The purification method according to claim 1 or 2, wherein the construction is performed with an interval of about 2 m to 5 m apart to maintain the proof strength of the purification ground.
【請求項4】 上記オーガにより汚染土壌層に鉄粉を吐
出混合するための掘削は、施工地面で見て各一回毎の施
工域の相互の間隔を、夫々約2m〜5m離間させて施工
することにより浄化地盤の耐力を保持することを特徴と
する請求項1又は2記載の浄化工法。
4. The excavation for discharging and mixing the iron powder into the contaminated soil layer by the auger is performed by setting a distance between each of the construction areas at each time of about 2 m to 5 m as viewed on the construction ground. The purification method according to claim 1 or 2, wherein the proof strength of the purification ground is maintained by doing.
【請求項5】 上記掘削のためのオーガは三軸式アース
オーガである請求項1〜4のいずれかに記載の浄化工
法。
5. The purification method according to claim 1, wherein the auger for excavation is a triaxial earth auger.
【請求項6】 請求項1の浄化工法において、汚染土壌
層中に吐出される鉄粉の量を掘削深度に対応して自由に
変更可能としたことを特徴とする浄化工法。
6. The purification method according to claim 1, wherein the amount of iron powder discharged into the contaminated soil layer can be freely changed according to the excavation depth.
JP2001075733A 2001-03-16 2001-03-16 Purification method of contaminated soil Pending JP2002273403A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001075733A JP2002273403A (en) 2001-03-16 2001-03-16 Purification method of contaminated soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001075733A JP2002273403A (en) 2001-03-16 2001-03-16 Purification method of contaminated soil

Publications (1)

Publication Number Publication Date
JP2002273403A true JP2002273403A (en) 2002-09-24

Family

ID=18932765

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001075733A Pending JP2002273403A (en) 2001-03-16 2001-03-16 Purification method of contaminated soil

Country Status (1)

Country Link
JP (1) JP2002273403A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004313997A (en) * 2003-04-18 2004-11-11 Eco-System Engineering Co Ltd Apparatus for purifying soil or ground-water contamination in situ
JP2005087800A (en) * 2003-09-12 2005-04-07 Dowa Mining Co Ltd Method for forming purification body for polluted groundwater
JP2006102591A (en) * 2004-10-01 2006-04-20 Dowa Mining Co Ltd Soil or ground water purifying method

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004313997A (en) * 2003-04-18 2004-11-11 Eco-System Engineering Co Ltd Apparatus for purifying soil or ground-water contamination in situ
JP2005087800A (en) * 2003-09-12 2005-04-07 Dowa Mining Co Ltd Method for forming purification body for polluted groundwater
JP4660690B2 (en) * 2003-09-12 2011-03-30 Dowaエコシステム株式会社 Method for forming a purified body for treating contaminated groundwater
JP2006102591A (en) * 2004-10-01 2006-04-20 Dowa Mining Co Ltd Soil or ground water purifying method

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