JP2000061442A - Method for cleaning soil and groundwater using granular cleaning material and its equipment - Google Patents

Method for cleaning soil and groundwater using granular cleaning material and its equipment

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Publication number
JP2000061442A
JP2000061442A JP10237135A JP23713598A JP2000061442A JP 2000061442 A JP2000061442 A JP 2000061442A JP 10237135 A JP10237135 A JP 10237135A JP 23713598 A JP23713598 A JP 23713598A JP 2000061442 A JP2000061442 A JP 2000061442A
Authority
JP
Japan
Prior art keywords
groundwater
horizontal well
soil
well hole
granular
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
JP10237135A
Other languages
Japanese (ja)
Inventor
Hitoshi Yamauchi
仁 山内
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.)
Kokusai Kogyo Co Ltd
Original Assignee
Kokusai 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 Kokusai Kogyo Co Ltd filed Critical Kokusai Kogyo Co Ltd
Priority to JP10237135A priority Critical patent/JP2000061442A/en
Publication of JP2000061442A publication Critical patent/JP2000061442A/en
Pending legal-status Critical Current

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  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Processing Of Solid Wastes (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To reduce and decompose contaminants with iron powder by using a granular cleaning material and widely sprinkling the cleaning material in a horizontal channel over a long distance. SOLUTION: At least one horizontal channel 8 is dug below a contaminated zone C, and then a granular purifying material 6 is incorporated into a semifluid body 7. The semifluid body 7 contg. the granular purifying material is forcedly poured into the horizontal channel 8 from an opening 5 of the channel 8 to widely sprinkle the granular purifying material in the channel 8. Otherwise, iron powder 6 is incorporated into a slurry ice water 13, and the slurry ice water 13 is forcedly poured into the horizontal well channel 8 from the opening 5 of the well channel 8.

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】本発明は鉄粉等の粒状浄化物
質を用いた土壌・地下水の浄化方法及びその設備に関
し、さらに詳細に言えば、メッキ工業やドライクリーニ
ング業、さらには半導体工業などで広く用いられるトリ
クロロエチレンやテトラクロロエチレンなどの塩素系揮
発性有機化合物により発生する土壌・地下水の汚染を浄
化するための土壌・地下水浄化方法及びその設備に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for purifying soil and groundwater using granular purification substances such as iron powder and its equipment, and more specifically, in the plating industry, dry cleaning industry, semiconductor industry, etc. The present invention relates to a soil / groundwater purification method and equipment for purifying soil / groundwater pollution generated by widely used chlorine-based volatile organic compounds such as trichlorethylene and tetrachloroethylene.

【0002】[0002]

【従来の技術】トリクロロエチレン、テトラクロロエチ
レン等の塩素系揮発性有機化合物は脱脂性に富むという
利点から、半導体工業、メッキ工業やクリーニング業な
どではこれらの塩素系揮発性有機化合物を広く用いてい
る。そして、これらの塩素系有機化合物が土壌に浸透す
ることによって土壌や地下水を汚染している。
2. Description of the Related Art Chlorine-based volatile organic compounds such as trichloroethylene and tetrachloroethylene are widely used in the semiconductor industry, plating industry, cleaning industry, etc., because they are rich in degreasing property. Then, these chlorine-based organic compounds permeate the soil to contaminate the soil and groundwater.

【0003】また、この汚染された地下水が飲料水とし
て用いられると、これらの塩素系揮発性有機化合物は人
体にがんを誘発する発がん性物質として作用した。その
他、カドミウム、鉛、水銀、6価クロム等の重金属やC
ODも土壌を汚染して、種々の問題を生じている。そし
て、汚染された土壌・地下水の浄化方法として、土壌吸
引法、揚水処理法、バイオレメディエーション、熱脱着
法、熱分解処理法などが従来から行われてきた。
When this contaminated groundwater is used as drinking water, these chlorine-based volatile organic compounds act as carcinogens that induce cancer in the human body. Other heavy metals such as cadmium, lead, mercury, hexavalent chromium, and C
OD also pollutes the soil, causing various problems. As a method for purifying contaminated soil / ground water, a soil suction method, a pumping treatment method, bioremediation, a thermal desorption method, a thermal decomposition method, etc. have been conventionally performed.

【0004】[0004]

【発明が解決しようとする課題】ところで、上記の従来
の土壌・地下水浄化方法は、実施条件が限定され、かつ
コストや処理期間を考慮してその効果を判断すると、汚
染サイトの状況によって浄化効果にバラツキがみられ
た。そのために、原位置で塩素系揮発性有機化合物など
の汚染物質を分解可能とする浄化技術の開発が求められ
ている。
By the way, the above-mentioned conventional soil and groundwater purification methods have limited implementation conditions, and if the effect is judged in consideration of cost and treatment period, the purification effect depends on the situation of the polluted site. There were variations. Therefore, development of a purification technology that can decompose pollutants such as chlorine-based volatile organic compounds in-situ is required.

【0005】しかし、原位置で塩素系揮発性有機化合物
などの汚染物質を分解させるには、浄化物質を汚染帯域
の広さに応じて撒布する必要があるために、汚染された
土壌を開削してトレンチや暗渠を形成し、これに浄化物
質を配置していたから、ばく大な費用を要した。しか
も、広範な汚染帯域が存在する場合には浄化物質を広範
囲に地中に送り込むことが必要となるが、これには限界
があり、土壌や地下水の汚染を十分に防止することは困
難であり、効果的な土壌・地下水の浄化対策を樹立する
ことは喫緊の課題であった。ところで、近時、鉄粉等の
粒状浄化物質による水溶液中で塩素系揮発性有機化合物
を分解処理する鉄粉法により浄化が行われるようになっ
てきた。この場合は、垂直井戸を用いて粒状浄化物質を
注入したり、あるいは地下水を揚水してから粒状浄化物
質を混ぜて浄化することが行われてきた。しかし、垂直
井戸では狭い範囲の地下水にしか鉄粉を混合させること
ができなかった。また、トレンチや暗渠は建築物やタン
クの下方に設置することはできず、しかも、深いトレン
チの施工は困難であった。
However, in order to decompose pollutants such as chlorine-based volatile organic compounds in-situ, it is necessary to spray a purification substance according to the size of the contamination zone. Since a trench and an underdrain were formed in this way and a purification substance was placed in this, it was extremely expensive. Moreover, in the case where there is a wide range of polluted zones, it is necessary to send purification substances into the ground in a wide range, but this is limited, and it is difficult to sufficiently prevent soil and groundwater pollution. Establishing effective soil and groundwater purification measures was an urgent issue. By the way, recently, purification has come to be performed by an iron powder method in which a chlorine-based volatile organic compound is decomposed in an aqueous solution of a granular purification substance such as iron powder. In this case, it has been practiced to inject a granular purification substance using a vertical well, or to pump groundwater and then mix the granular purification substance for purification. However, in vertical wells, iron powder could only be mixed with a small amount of groundwater. Moreover, the trench and the underdrain cannot be installed under the building or the tank, and it is difficult to construct the deep trench.

【0006】本発明の目的は、かかる従来の問題点を解
決するためになされたもので、粒状浄化物質を用い、さ
らに該粒状浄化物質を水平井戸孔に長い距離にわたって
広範に撒布することにより、粒状浄化物質により汚染物
質を還元分解させるようにした土壌・地下水の浄化方法
及びその設備を提供することにある。
The object of the present invention is to solve the above-mentioned conventional problems, and by using a granular purification substance, and further by spreading the granular purification substance over a horizontal well hole over a long distance, It is an object of the present invention to provide a soil / groundwater purification method and equipment for reducing and decomposing pollutants by granular purification substances.

【0007】[0007]

【課題を解決するための手段】本発明は、鉄粉などの粒
状浄化物質による水溶液中での塩素系揮発性有機化合物
などの汚染物質の原位置分解処理が可能であるという知
見に基づきなされた、粒状浄化物質を用いた土壌・地下
水の浄化方法及びその設備であり、前述した技術的課題
を解決するために以下のように構成されている。
The present invention was made based on the finding that it is possible to perform in-situ decomposition treatment of pollutants such as chlorine-based volatile organic compounds in an aqueous solution with a granular purification substance such as iron powder. A method for purifying soil and groundwater using a granular purifying substance and its equipment, which are configured as follows in order to solve the above-mentioned technical problems.

【0008】すなわち、本発明の粒状浄化物質を用いた
土壌・地下水の浄化方法は、汚染帯域の下方に少なくと
も1本の水平井戸孔を掘削し、次いで粒状浄化物質を半
流動体に含ませ、該粒状浄化物質を含む半流動体を前記
水平井戸孔の開口部から前記水平井戸孔内に強制的に注
入し、土壌や地下水に浸透する塩素系有機化合物などの
有害物質を還元分解させることを特徴とする(請求項
1)。
That is, in the method for purifying soil / ground water using the granular purification substance of the present invention, at least one horizontal well hole is drilled below the contaminated zone, and then the granular purification substance is contained in the semi-fluid body, A semi-fluid containing the granular purification material is forcibly injected into the horizontal well hole from the opening of the horizontal well hole to reduce and decompose harmful substances such as chlorine-based organic compounds that permeate into soil and groundwater. It is characterized (Claim 1).

【0009】なお、粒状浄化物質は鉄粉が好ましい。そ
の他にシリコンなどを用いることができる。水平井戸孔
は通常は掘削したままでよいが、土壌が崩壊しやすい性
質の場合には、多数の孔を穿設した筒状の井戸材料を前
記水平井戸孔の内部に挿通することにより該水平井戸孔
の崩壊を防止することもできる。
Iron powder is preferable as the particulate purification substance. Besides, silicon or the like can be used. Normally, the horizontal well hole may be left excavated, but if the soil tends to collapse, the horizontal well hole may be formed by inserting a tubular well material with a large number of holes into the horizontal well hole. It is also possible to prevent the collapse of the well hole.

【0010】また、半流動体には、当初は粘性の強い流
体であるが、時間の経過と共に粘性が小さくなり、水状
となって地下水に溶けこんでなくなり、浄化物質である
鉄粉や、鉄粉を主体とする浄化物質だけを井戸内に残存
させるようなゲル状の物質、例えば泥水材料であるポリ
マー、あるいはゼリー状の物質を用いることが好まし
い。
Further, the semi-fluid body is a fluid having a high viscosity at first, but the viscosity becomes smaller with the lapse of time and becomes a water state so that it is not dissolved in the ground water, and iron powder which is a purification substance, It is preferable to use a gel-like substance, such as a polymer which is a muddy water material, or a jelly-like substance, in which only the purification substance mainly containing iron powder remains in the well.

【0011】さらに、本発明の粒状浄化物質を用いた土
壌・地下水の浄化方法は、汚染帯域の下方に少なくとも
1本の水平井戸孔を掘削し、次いで粒状浄化物質をスラ
リー状の氷水に含ませ、該氷水に含まれた前記粒状浄化
物質を前記水平井戸孔の開口部から前記水平井戸孔内に
強制的に注入し、土壌や地下水に浸透する塩素系揮発性
有機化合物などの有害物質を還元分解させることを特徴
とする(請求項2)。
Further, in the method for purifying soil / ground water using the granular purification substance of the present invention, at least one horizontal well hole is drilled below the contaminated zone, and then the granular purification substance is contained in slurry ice water. , Forcibly injecting the granular purification substance contained in the ice water into the horizontal well hole from the opening of the horizontal well hole to reduce harmful substances such as chlorine-based volatile organic compounds that permeate into soil and groundwater It is characterized in that it is decomposed (claim 2).

【0012】なお、スラリー状の氷水には、エチレング
リコールやプロピレングリコールなどの2価アルコール
の水溶液である有機ブラインを凍結させ、凍結の進行に
伴って氷を析出させたことにより氷水を生成したものを
用いるのが好ましい。しかし、塩の水溶液を用いること
もできることはもちろんである。
The ice water in the form of slurry is produced by freezing organic brine, which is an aqueous solution of a dihydric alcohol such as ethylene glycol or propylene glycol, and precipitating ice as the freezing progresses. Is preferably used. However, it goes without saying that an aqueous solution of salt can be used.

【0013】本発明は粒状浄化物質を用いた土壌・地下
水の浄化設備であり、前述の技術的課題を解決するため
に以下のように構成されている。すなわち、汚染帯域の
下方に掘削された少なくとも1本の水平井戸孔と、該水
平井戸孔に撒布された粒状浄化物質とを備え、土壌や地
下水に浸透する塩素系揮発性有機化合物などの有害物質
を還元分解可能とすることを特徴とする(請求項3)。
The present invention is a soil / groundwater purification facility using a granular purification substance, and is configured as follows in order to solve the above-mentioned technical problems. That is, at least one horizontal well hole excavated below the polluted zone and a granular purification substance sprinkled in the horizontal well hole are provided, and harmful substances such as chlorine-based volatile organic compounds that permeate soil and groundwater. Is reducible and decomposable (claim 3).

【0014】[0014]

【作用】本発明の粒状浄化物質を用いた土壌・地下水の
浄化方法及びその設備によると、鉄粉などの粒状浄化物
質は土壌・地下水においてその水溶液中で塩素系揮発性
有機化合物を原位置で分解処理を行う。さらに、この粒
状浄化物質に還元剤を混合することによって塩素系揮発
性有機化合物などの汚染物質の分解処理を促進する。
[Operation] According to the method for purifying soil and groundwater using the granular purification substance of the present invention and the equipment therefor, the granular purification substance such as iron powder is a chlorinated volatile organic compound in situ in the aqueous solution in soil and groundwater. Perform disassembly processing. Furthermore, by mixing a reducing agent with the particulate purification substance, the decomposition treatment of pollutants such as chlorine-based volatile organic compounds is promoted.

【0015】[0015]

【発明の実施の形態】以下、本発明の粒状浄化物質を用
いた土壌・地下水の浄化設備を図に示される実施形態に
ついてさらに詳細に説明する。ただし、この実施の形態
に記載されている構成部品の寸法、材質、形状、その相
対的配置などは特に特定的な記載がない限りは、この発
明の範囲をそれのみに限定する趣旨ではなく、単なる説
明例にすぎない。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, a soil / groundwater purification facility using the granular purification material of the present invention will be described in more detail with reference to the embodiments shown in the drawings. However, unless otherwise specified, the dimensions, materials, shapes, and relative arrangements of the components described in this embodiment are not intended to limit the scope of the present invention thereto, It is just an example of explanation.

【0016】(第1の実施の形態)図1は本発明の実施
形態の水平井戸孔の掘削状態を示す説明図であり、図2
は第1の実施形態に係る鉄粉を用いる土壌・地下水の浄
化設備を概略を示す。また、図5はこの実施形態の水平
井戸孔の断面を示す。
(First Embodiment) FIG. 1 is an explanatory view showing an excavated state of a horizontal well hole according to an embodiment of the present invention.
Shows an outline of a soil / groundwater purification facility using iron powder according to the first embodiment. Further, FIG. 5 shows a cross section of the horizontal well hole of this embodiment.

【0017】まず、水平井戸孔を掘削するには、図1に
示すように塩素系揮発性有機化合物であるトリクロロエ
チレンによる汚染帯域Cの下方に所定の区間を隔てて両
端に小ピットを穿設して一方を貫入坑1とし、他方を到
達坑2とする。次いで、ロッド3の先端に掘削用工具で
あるドリル4を取り付け、駆動源であるパワーユニット
トラック25を駆動してロッド3をドリルユニット16
で案内しながら回転させ、地下水面WLに向けて該ドリ
ル4を回転駆動する。すると、ドリル4は回転しながら
地中Eの帯水層を略水平方向に掘進する。ドリル4が到
達坑2に達したらドリルの回転を停止し、掘進を完了す
る。
First, in order to excavate a horizontal well hole, small pits are formed at both ends below a contaminated zone C by a chlorine-based volatile organic compound, trichlorethylene, at predetermined intervals as shown in FIG. One is called a penetration pit 1 and the other is a reaching pit 2. Next, the drill 4 which is a drilling tool is attached to the tip of the rod 3, and the power unit track 25 which is a drive source is driven to move the rod 3 into the drill unit 16.
The guide 4 is rotated while being guided, and the drill 4 is rotationally driven toward the water table WL. Then, the drill 4 excavates the aquifer in the underground E in a substantially horizontal direction while rotating. When the drill 4 reaches the reaching pit 2, the rotation of the drill is stopped and the excavation is completed.

【0018】次いで、到達坑2でドリル4をロッド3か
ら取り外し、貫入坑1と到達坑2を埋め戻し、図に示す
ような一端に開口部5を備え、他端を閉止した水平井戸
8を構築する。なお、この水平井戸8は汚染帯域Cの広
さに応じて図5に示すように複数個所に平行に配置す
る。
Then, the drill 4 is removed from the rod 3 at the reaching pit 2, the penetration pit 1 and the reaching pit 2 are backfilled, and a horizontal well 8 having an opening 5 at one end and the other end closed as shown in the figure is formed. To construct. The horizontal wells 8 are arranged in parallel at a plurality of places according to the size of the contamination zone C as shown in FIG.

【0019】本実施の形態において粒状浄化物質として
鉄粉を用いたが、該鉄粉は表1に示すような成分組成及
び物性のものを例示することができるが、本実施の形態
においては、そのうちで表面積が最大の同和鉄粉株式会
社製の鉄粉E−200を使用した。なお、DE、DNC
−240は同和鉄粉株式会社製の鉄粉、鋳鉄粉は和光純
薬工業株式会社製のものである。
In the present embodiment, iron powder was used as the particulate purification substance. The iron powder may have the composition and physical properties shown in Table 1, but in the present embodiment, Among them, iron powder E-200 manufactured by Dowa Iron Powder Co., Ltd. having the largest surface area was used. In addition, DE, DNC
-240 is iron powder manufactured by Dowa Iron Powder Co., Ltd., and cast iron powder is manufactured by Wako Pure Chemical Industries, Ltd.

【0020】[0020]

【表1】 [Table 1]

【0021】次いで、図2に示すように前記の鉄粉6
(図中誇張して示してある)を半流動体としての泥水材
料であるポリマー7(商品名BioBore)に含ませ
たものを、開口部5から矢印で示すように水平井戸孔8
内に圧入した。さらに、回転ポンプPを用いて鉄粉6を
含むポリマー7に高圧を付加して容器15から水平井戸
孔へ鉄粉を圧入する。
Then, as shown in FIG.
Polymer 7 (trade name: BioBore), which is a muddy water material as a semi-fluid, is included in the horizontal well hole 8 as shown by an arrow from the opening 5 (shown in an exaggerated manner in the figure).
Pressed in. Further, a high pressure is applied to the polymer 7 containing the iron powder 6 by using the rotary pump P to press the iron powder from the container 15 into the horizontal well hole.

【0022】すると、鉄粉6を含むポリマー7は当初は
粘性の強い物質であるから、水平井戸孔8内を流動しな
が鉄粉6を該水平井戸孔8の端部から他端部まで流動し
て鉄粉6を井戸孔の奥まで運搬する。このため、鉄粉6
は井戸孔内に広範に撒布されたことになる。
Then, since the polymer 7 containing the iron powder 6 is a substance having a strong viscosity at the beginning, the iron powder 6 is not flowed in the horizontal well hole 8 from the end of the horizontal well hole 8 to the other end thereof. It flows and conveys the iron powder 6 to the back of the well hole. Therefore, iron powder 6
Has been widely spread in the well hole.

【0023】そして、ポリマー7は時間の経過に伴って
は水状となり地下水に溶けこんでなくなり、鉄粉6だけ
が井戸孔8内に残存することになる。その結果、鉄粉6
は汚染帯域Cを経て地中Eに浸透する重力水に含まれる
トリクロロエチレンを還元分解して、トリクロロエチレ
ン(TCE)の濃度は時間に対し指数関数的に減少する
ことになり、土壌の浄化と地下水の汚染が防止される。
Then, the polymer 7 becomes water-like with the passage of time and is not dissolved in the groundwater, and only the iron powder 6 remains in the well hole 8. As a result, iron powder 6
Decompresses trichlorethylene contained in gravity water that penetrates underground E through pollution zone C, and the concentration of trichlorethylene (TCE) will decrease exponentially with time. Contamination is prevented.

【0024】(第2の実施の形態)図3は本発明の第2
の実施形態の水平井戸孔の掘削状態を示す概略図であ
る。そして、図5はこの実施形態の水平井戸孔の断面を
示す。この水平井戸81を掘削するには、図1に示すよ
うに所定の区間を隔てて両端に小ピットを穿設して一方
を貫入坑1とし、他方を到達坑2とする。次いで、ロッ
ド3の先端にドリル4を取り付け、パワーユニットトラ
ック25を駆動してロッド3をドリルユニット16で案
内しながら回転させ、地下水面WLに向けてドリル4を
回転駆動する。すると、ドリル4は回転しながら地中E
の帯水層を略水平方向に掘進する。ドリル4が到達坑2
に至ると回転を停止させ、水平井戸孔81を掘削する。
(Second Embodiment) FIG. 3 shows a second embodiment of the present invention.
It is a schematic diagram showing a state of excavation of a horizontal well hole of the embodiment. 5 shows a cross section of the horizontal well hole of this embodiment. In order to excavate the horizontal well 81, small pits are bored at both ends of a predetermined section as shown in FIG. 1 so that one is a penetration pit 1 and the other is a reaching pit 2. Next, the drill 4 is attached to the tip of the rod 3, the power unit track 25 is driven, the rod 3 is rotated while being guided by the drill unit 16, and the drill 4 is rotationally driven toward the water table WL. Then, the drill 4 rotates E
The aquifer is dug in a substantially horizontal direction. Drill 4 reached 2
Then, the rotation is stopped and the horizontal well hole 81 is excavated.

【0025】次いで、ロッド3の先端に前記ドリル4と
反対方向に拡孔のためのリーマ(図示せず)を取り付け
とともに、リーマの後方に円筒状の井戸材料9を取り付
けて、ロッド3を回転駆動させてリーマを回転させなが
ら、多数の孔を設けた筒状の井戸材料9を井戸孔の掘削
方向とは反対方向(図1にの右側から左側へ)にロッド
3を引っ張ることにより、井戸材料9を井戸孔81に挿
入する。
Then, a reamer (not shown) for expanding a hole is attached to the tip of the rod 3 in the direction opposite to the drill 4, and a cylindrical well material 9 is attached to the rear of the reamer to rotate the rod 3. While rotating the reamer by driving, the tubular well material 9 provided with a large number of holes is pulled by pulling the rod 3 in the direction opposite to the drilling direction of the well holes (from the right side to the left side in FIG. 1). The material 9 is inserted into the well hole 81.

【0026】次いで、貫入坑1と到達坑2を埋め戻し、
図3に示すように水平井戸孔81に通ずる一対の開口部
5a、5bを有する水平井戸孔81を構築する。なお、
この水平井戸81も汚染帯域Cの広さに応じて図5に示
すように複数個所に平行に配置する。
Then, the penetration pit 1 and the reaching pit 2 are backfilled,
As shown in FIG. 3, a horizontal well hole 81 having a pair of openings 5a and 5b communicating with the horizontal well hole 81 is constructed. In addition,
The horizontal wells 81 are also arranged in parallel at a plurality of places depending on the size of the contamination zone C as shown in FIG.

【0027】本実施の形態においても粒状浄化物質とし
ての鉄粉6には、表1に示す鉄粉のうち最も比表面積の
大きなE−200を用いる。そして、この鉄粉を弱酸性
の還元物質である粉状の重亜硫酸ナトリウム(NaHS
O3)と混合する。この混合鉄粉をエチレングリコールの
水溶液であるブラインに混合した後、製氷機10に充填
する。製氷機10内ではブラインは凍結の進行に伴って
鉄粉を含む氷を析出し、スラリー状の氷水13が生成さ
れる。
Also in this embodiment, E-200 having the largest specific surface area among the iron powders shown in Table 1 is used as the iron powder 6 as the granular purification substance. Then, this iron powder is powdered sodium bisulfite (NaHS) which is a weakly acidic reducing substance.
Mix with O3). The mixed iron powder is mixed with brine, which is an aqueous solution of ethylene glycol, and then charged into the ice maker 10. In the ice making machine 10, brine precipitates ice containing iron powder as freezing progresses, and ice water 13 in the form of a slurry is generated.

【0028】前記のように生成された鉄粉を含む氷12
とスラリー状の氷水13は蓄熱層11に送られ、さらに
ポンプPによって高圧を付加されて水平井戸孔81に圧
送される。そのため、スラリー状の氷水は井戸内を流動
して水平井戸孔8内に深く流入する。氷は時間の経過と
共に次第に融解して地下水に溶け込み、その後に鉄粉6
が水平井戸孔81内に残存し、広範に撒布された状態に
なる。
Ice 12 containing iron powder produced as described above
The ice water 13 in the form of slurry is sent to the heat storage layer 11, is further pressurized by the pump P, and is sent to the horizontal well hole 81 under pressure. Therefore, the slurry ice water flows in the well and deeply flows into the horizontal well hole 8. The ice gradually melts with the passage of time and melts into the groundwater, after which iron powder 6
Remain in the horizontal well hole 81, and are spread over a wide area.

【0029】さらに、粒状浄化物質としての鉄粉には弱
酸性の還元物質である重亜硫酸ナトリウム(NaHSO
3)が混合しているため、水溶液中の溶存酸素DOの存在
による酸化鉄や、あるいは塩基性域における水酸化鉄に
より不動態化することがない。このために、トリクロロ
エチレン、テトラクロロエチレンなどの汚染物質の分解
反応が阻止されることがなく、鉄粉による塩素系揮発性
有機化合物の還元分解反応が促進され、土壌・地下水の
効率的な浄化が行われる。
Further, iron powder as a granular purification substance is a weakly acidic reducing substance such as sodium bisulfite (NaHSO).
Since 3) is mixed, it is not passivated by iron oxide due to the presence of dissolved oxygen DO in the aqueous solution or iron hydroxide in the basic region. For this reason, the decomposition reaction of pollutants such as trichlorethylene and tetrachloroethylene is not blocked, the reductive decomposition reaction of chlorine-based volatile organic compounds by the iron powder is promoted, and the soil and groundwater are efficiently purified. .

【0030】(第3の実施の形態)図4は本実施の形態
の断面を示し、第1の実施の形態と同一の井戸孔が地下
水面WLの上方に構築されている。従って、本実施の形
態では水平井戸孔8の掘削方法は第1の実施の形態と同
一であるので、掘削方法についての説明は省略する。
表1に示す鉄粉のうち、E−200を用い、これに低塩
基性の還元剤である亜硫酸ナトリウム(Na22SO3)
を混合する。
(Third Embodiment) FIG. 4 shows a cross section of the present embodiment, in which the same well hole as that of the first embodiment is constructed above the water table WL. Therefore, in the present embodiment, the method of excavating the horizontal well hole 8 is the same as that of the first embodiment, and therefore the description of the excavation method is omitted.
Of the iron powders shown in Table 1, E-200 was used and a low-basic reducing agent, sodium sulfite (Na2 2 SO3), was used.
To mix.

【0031】次いで、粒状浄化物質としての鉄粉6を半
流動体としてのゼリー状の半流動体71に含ませて、開
口部5から矢印で示すように水平井戸孔8内に圧入し
た。さらに、回転ポンプPを用いて鉄粉6を含むゼリー
状の半流動体71に高圧を付加して容器15から水平井
戸孔8に圧入する。
Next, the iron powder 6 as a granular purification substance was contained in the jelly-like semi-fluid body 71 as a semi-fluid body, and was pressed into the horizontal well hole 8 from the opening 5 as shown by the arrow. Further, a high pressure is applied to the jelly-like semi-fluid 71 containing the iron powder 6 by using the rotary pump P, and the jelly-like semi-fluid 71 is pressed into the horizontal well hole 8 from the container 15.

【0032】鉄粉6を含むゼリー71は当初は粘性の強
い物質であるが、水平井戸孔8内を流動しなが鉄粉6を
該水平井戸8の端部から他端部まで流動して鉄粉6を運
搬する。このため、鉄粉6は井戸孔内に広範に撒布され
る。
The jelly 71 containing the iron powder 6 is a substance having a strong viscosity at first, but the iron powder 6 does not flow in the horizontal well hole 8 but flows from the end of the horizontal well 8 to the other end thereof. Carry iron powder 6. Therefore, the iron powder 6 is widely spread in the well holes.

【0033】そして、ゼリー71は時間の経過に伴って
は水状となり地下水に溶けこんでなくなり、鉄粉6だけ
が井戸孔8内に残存する。その結果、鉄粉6は汚染帯域
Cを経て地中Eに浸透する重力水に含まれるテトラクロ
ロエチレンを還元分解する。
Then, the jelly 71 becomes water-like with the passage of time and does not dissolve in the groundwater, and only the iron powder 6 remains in the well hole 8. As a result, the iron powder 6 reductively decomposes tetrachloroethylene contained in gravity water that permeates the ground E through the pollution zone C.

【0034】[0034]

【発明の効果】以上説明したように、本発明の粒状浄化
物質を用いた土壌・地下水の浄化方法及びその設備によ
れば、塩素系揮発性有機化合物などによる土壌・地下水
の汚染に対する浄化能力のある鉄粉は、半流動体やスラ
リー状氷水によって水平井戸孔内に広い範囲にわたって
撒布することができるから、塩素系揮発性有機化合物な
どの汚染物質を広範に捕捉して還元分解反応が行われ
る。しかも、粒状浄化物質である鉄粉に亜硫酸ナトリウ
ムや重亜硫酸ナトリウムなどの還元剤を混合することに
よって有害物質の還元分解がより一層促進される。
As described above, according to the soil / groundwater purification method and the equipment using the granular purification material of the present invention, the purification ability for soil / groundwater contamination by chlorine-based volatile organic compounds, etc. A certain iron powder can be spread over a wide area in a horizontal well hole by a semi-fluid or slurry ice water, so that pollutants such as chlorine-based volatile organic compounds are widely captured and reductive decomposition reaction is performed. . Moreover, the reductive decomposition of harmful substances is further promoted by mixing iron powder, which is a granular purification substance, with a reducing agent such as sodium sulfite or sodium bisulfite.

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

【図1】本発明の実施形態の水平井戸孔の掘削状態を示
す説明図である。
FIG. 1 is an explanatory diagram showing an excavated state of a horizontal well hole according to an embodiment of the present invention.

【図2】本発明の第1の実施形態に係る土壌・地下水の
浄化設備の概略図である。
FIG. 2 is a schematic diagram of a soil / groundwater purification facility according to the first embodiment of the present invention.

【図3】本発明の第2の実施形態に係る土壌・地下水の
浄化設備の概略図である。
FIG. 3 is a schematic diagram of a soil / groundwater purification facility according to a second embodiment of the present invention.

【図4】本発明の第3の実施形態に係る土壌・地下水の
浄化設備の概略図である。
FIG. 4 is a schematic diagram of a soil / groundwater purification facility according to a third embodiment of the present invention.

【図5】各実施形態の土壌浄化設備の横断面図である。FIG. 5 is a cross-sectional view of the soil purification equipment of each embodiment.

【符号の説明】[Explanation of symbols]

5、5a、5b 開口部 6 鉄粉(粒状浄化物質) 7 半流動体(ポリマー) 8 水平井戸孔 13 スラリー状の氷水 C 汚染帯域 5, 5a, 5b openings 6 Iron powder (granular purification substance) 7 Semi-fluid (polymer) 8 horizontal well holes 13 Slurry ice water C pollution zone

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 汚染帯域の下方に少なくとも1本の水平
井戸孔を掘削し、次いで粒状浄化物質を半流動体に含ま
せ、該粒状浄化物質を含む半流動体を前記水平井戸孔の
開口部から前記水平井戸孔内に強制的に注入し、土壌や
地下水に浸透する塩素系有機化合物などの有害物質を還
元分解させることを特徴とする粒状浄化物質を用いた土
壌・地下水の浄化方法。
1. At least one horizontal well hole is drilled below the contaminated zone, and then the particulate purification material is contained in a semi-fluid, and the semi-fluid containing the particulate purification material is opened in the opening of the horizontal well hole. A method for purifying soil / groundwater using a granular purifying substance, which comprises forcibly injecting into the horizontal well hole to reduce and decompose harmful substances such as chlorine-based organic compounds that permeate into soil and groundwater.
【請求項2】 汚染帯域の下方に少なくとも1本の水平
井戸孔を掘削し、次いで粒状浄化物質をスラリー状の氷
水に含ませ、該氷水に含まれた前記粒状浄化物質を前記
水平井戸孔の開口部から前記水平井戸孔内に強制的に注
入し、土壌や地下水に浸透する塩素系揮発性有機化合物
などの有害物質を還元分解させることを特徴とする粒状
浄化物質を用いた土壌・地下水の浄化方法。
2. At least one horizontal well hole is drilled below the contaminated zone, and then the granular purification material is contained in slurry ice water, and the granular purification material contained in the ice water is contained in the horizontal well hole. Soil and groundwater using granular purification substances characterized by reducing and decomposing harmful substances such as chlorine-based volatile organic compounds that permeate into soil and groundwater by forcibly injecting into the horizontal well hole from the opening Purification method.
【請求項3】 汚染帯域の下方に掘削された少なくとも
1本の水平井戸孔と、該水平井戸孔に撒布された粒状浄
化物質とを備え、土壌や地下水に浸透する塩素系揮発性
有機化合物などの有害物質を還元分解可能とすることを
特徴とする粒状浄化物質を用いた土壌・地下水の浄化設
備。
3. A chlorine-based volatile organic compound, etc., which comprises at least one horizontal well hole excavated below the contaminated zone and a granular purification substance sprinkled in the horizontal well hole, and which permeates soil and groundwater. Soil / groundwater purification equipment using granular purification substances, which is capable of reducing and decomposing the harmful substances of.
JP10237135A 1998-08-24 1998-08-24 Method for cleaning soil and groundwater using granular cleaning material and its equipment Pending JP2000061442A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10237135A JP2000061442A (en) 1998-08-24 1998-08-24 Method for cleaning soil and groundwater using granular cleaning material and its equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10237135A JP2000061442A (en) 1998-08-24 1998-08-24 Method for cleaning soil and groundwater using granular cleaning material and its equipment

Publications (1)

Publication Number Publication Date
JP2000061442A true JP2000061442A (en) 2000-02-29

Family

ID=17010932

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10237135A Pending JP2000061442A (en) 1998-08-24 1998-08-24 Method for cleaning soil and groundwater using granular cleaning material and its equipment

Country Status (1)

Country Link
JP (1) JP2000061442A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002254061A (en) * 2001-02-28 2002-09-10 Shimizu Corp In situ clarification method and equipment for combined pollution soil
KR20030012177A (en) * 2001-07-30 2003-02-12 주식회사 한화건설 Contaminated soil remediation method using horizontal remediation well method
JP2004195375A (en) * 2002-12-19 2004-07-15 Ohbayashi Corp Water supply method in bentonite filled water barrier mat construction method
JP2004290768A (en) * 2003-03-26 2004-10-21 Ataka Construction & Engineering Co Ltd Method for cleaning soil and ground water polluted with organochlorine compound
JP2010264399A (en) * 2009-05-15 2010-11-25 Shimizu Corp Resoiling preventing method after contaminated soil cleaning
CN113522956A (en) * 2021-07-15 2021-10-22 北京建工环境修复股份有限公司 Horizontal well with prefabricated filter material

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002254061A (en) * 2001-02-28 2002-09-10 Shimizu Corp In situ clarification method and equipment for combined pollution soil
KR20030012177A (en) * 2001-07-30 2003-02-12 주식회사 한화건설 Contaminated soil remediation method using horizontal remediation well method
JP2004195375A (en) * 2002-12-19 2004-07-15 Ohbayashi Corp Water supply method in bentonite filled water barrier mat construction method
JP2004290768A (en) * 2003-03-26 2004-10-21 Ataka Construction & Engineering Co Ltd Method for cleaning soil and ground water polluted with organochlorine compound
JP2010264399A (en) * 2009-05-15 2010-11-25 Shimizu Corp Resoiling preventing method after contaminated soil cleaning
CN113522956A (en) * 2021-07-15 2021-10-22 北京建工环境修复股份有限公司 Horizontal well with prefabricated filter material

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