JP4360157B2 - Purification method and system for hardly air permeable and contaminated soil - Google Patents

Purification method and system for hardly air permeable and contaminated soil Download PDF

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JP4360157B2
JP4360157B2 JP2003307444A JP2003307444A JP4360157B2 JP 4360157 B2 JP4360157 B2 JP 4360157B2 JP 2003307444 A JP2003307444 A JP 2003307444A JP 2003307444 A JP2003307444 A JP 2003307444A JP 4360157 B2 JP4360157 B2 JP 4360157B2
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和男 峠
道彦 石田
洋二 石川
治彦 藤井
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Obayashi Corp
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Description

本発明は、難透気透水性汚染土壌に存在する汚染物質を回収浄化する浄化方法及びシステムに関する。   The present invention relates to a purification method and system for recovering and purifying contaminants present in hardly permeable and air permeable contaminated soil.

工場跡地の土壌内には、トリクロロエチレンなどで代表される揮発性有機塩素化合物、燃料油や機械油、ダイオキシン類、あるいはカドミウム、鉛、銅、亜鉛、ニッケル、クロムなどの重金属といったさまざまな汚染物質が土壌に混入していることがある。   Various pollutants such as volatile organic chlorine compounds such as trichlorethylene, fuel oils and machine oils, dioxins, and heavy metals such as cadmium, lead, copper, zinc, nickel and chromium are found in the soil of the factory site. May be in the soil.

かかる汚染物質で汚染された汚染土をそのまま放置すると、該土に混入している汚染物質が周囲に拡散し、周辺住民の生活に支障を来すとともに、雨水によって土粒子から遊離した場合には、地下水等に混入して水質を汚濁させる原因ともなる。そのため、上述した汚染物質で汚染された土については、さまざまな方法を使って浄化しなければならない。   If the contaminated soil contaminated with such contaminants is left as it is, the contaminants mixed in the soil will diffuse to the surroundings, hindering the lives of the surrounding residents, and if they are released from the soil particles by rainwater In addition, it may cause contamination of groundwater by contaminating water quality. Therefore, the soil contaminated with the above-mentioned pollutants must be cleaned using various methods.

土壌内の汚染物質を原位置で浄化処理する方法としては、従来からさまざまな方法が開発されており、土壌ガス吸引法、汚染土壌に注水しこれを揚水して地上で処理するいわゆる通水洗浄法、空気を送り込んでその気泡に汚染物質を連行させる、いわゆる気泡連行浄化法、空気圧入とガス吸引を組み合わせたエアスパージング法、土中菌の微生物活性を利用したバイオレメディエーションによる方法など多種多様な方法が知られている。   Various methods have been developed to purify pollutants in the soil in-situ, so-called water-cleaning methods that use the soil gas suction method, injecting water into the contaminated soil, pumping it up, and treating it on the ground. Various methods, such as the so-called bubble entrainment purification method, in which air is introduced and entrained pollutants in the bubbles, the air sparging method that combines pneumatic injection and gas suction, and the bioremediation method that utilizes the microbial activity of soil fungi The method is known.

特開2002−119952号公報JP 2002-119952 A 特開2001−205248号公報JP 2001-205248 A

しかしながら、汚染物質が粘土層やシルト層といった難透気透水層に存在する場合には上述した方法を採用することができない。すなわち、これらの難透気透水層は、透気性及び透水性が悪いため、汚染物質が入り込む懸念は比較的少ないものの、かかる難透気透水層にいったん汚染物質が混入すると、上述したように透気性及び透水性が悪いことがかえって浄化の支障となり、難透気透水層内から汚染物質を回収することがきわめて困難になるという問題を生じていた。   However, when the pollutant is present in a hardly air permeable water permeable layer such as a clay layer or a silt layer, the above-described method cannot be employed. That is, since these hardly permeable air permeable layers have poor air permeability and water permeability, there is relatively little concern about the entry of contaminants. However, once the contaminants are mixed into the hardly permeable air permeable layer, as described above. On the other hand, the poor tempering and water permeability impeded purification, which caused the problem that it was very difficult to recover the pollutants from the hardly permeable air permeable layer.

本発明は、上述した事情を考慮してなされたもので、難透気透水層に存在する汚染物質を確実かつ効率的に回収可能な難透気透水性汚染土壌の浄化方法及びシステムを提供することを目的とする。   The present invention has been made in consideration of the above-described circumstances, and provides a purification method and system for hardly permeable and air permeable contaminated soil capable of reliably and efficiently recovering contaminants present in the hardly permeable and air permeable layer. For the purpose.

上記目的を達成するため、本発明に係る難透気透水性汚染土壌の浄化方法は、地下水位より上に存在する不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に振動体を埋設し、該振動体の駆動操作によって前記汚染領域内の土粒子に振動を付与し、該汚染領域に圧入され又は自然流入した空気に前記汚染物質を連行させながら前記汚染物質を前記空気とともに該汚染領域の上方に設けた吸引管により吸引し浄化処理を行うものであって、前記振動体を、下端が前記汚染領域に埋設される杭又は矢板と、該杭又は矢板の上端に取り付けられるバイブロハンマーとで構成したことを特徴とする。 In order to achieve the above object, the method of purifying hardly permeable and air permeable contaminated soil according to the present invention is applied to a contaminated area contaminated with a pollutant in the unsaturated permeable and air permeable layer existing above the groundwater level. An oscillating body is embedded, and vibrations are applied to the soil particles in the contaminated area by driving the oscillating body, and the contaminants are entrained in the air that is pressed into the contaminated area or naturally flows into the contaminated area. A suction pipe provided above the contaminated area together with air to perform purification treatment , the vibrating body is a pile or sheet pile whose lower end is buried in the contaminated area, and an upper end of the pile or sheet pile It is characterized by comprising a vibro hammer to be attached.

本発明に係る難透気透水性汚染土壌の浄化方法は、地下水位より上に存在する不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に振動体を埋設し、該振動体の駆動操作によって前記汚染領域内の土粒子に振動を付与し、該汚染領域に圧入され又は自然流入した空気に前記汚染物質を連行させながら前記汚染物質を前記空気とともに該汚染領域の上方に設けた吸引管により吸引し浄化処理を行うものであって、前記振動体をバイブレータで構成したことを特徴とするIn the method of purifying hardly permeable and air permeable contaminated soil according to the present invention, an oscillating body is embedded in a contaminated area contaminated with a contaminant in the unsaturated permeable and air permeable layer existing above the groundwater level, Vibration is applied to the soil particles in the contaminated area by driving the vibrating body, and the contaminants are taken together with the air above the contaminated area while entraining the pollutants in the air that is press-fitted into the contaminated area or naturally flows in. be one that performs suction and purification treatment by a suction pipe provided in, characterized in that the vibrating body constituted by a vibrator.

本発明に係る難透気透水性汚染土壌の浄化システムは、地下水位より上に存在する不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に埋設され駆動操作によって前記汚染領域内の土粒子に振動を付与する振動体と、該汚染領域に圧入され又は自然流入した空気に連行された汚染物質を該空気とともに該汚染領域の上方に設けた吸引管により吸引し浄化処理を行うガス処理設備とを備えたものであって、前記汚染領域に空気を圧入する空気圧入機構を備えるとともに、該空気圧入機構を、空気吐出口が前記不飽和難透気透水層の汚染領域に位置するように埋設される圧入管と、空気タンクを介して該圧入管に接続されたエアコンプレッサーとから構成したことを特徴とするThe system for purifying hardly permeable and air permeable contaminated soil according to the present invention includes the unsaturated hardly permeable and air permeable layer existing above the groundwater level, embedded in a contaminated area contaminated with a contaminant and driven by the operation. A vibrating body that imparts vibrations to the soil particles in the region, and a contaminant that is entrained in the air that is press-fitted into the contaminated region or that naturally flows into the region, is sucked together with the air by a suction pipe provided above the contaminated region, and is purified. be those with a gas treatment facility for performing, provided with a pneumatic input mechanism of injecting air into the contaminated region, the air press fit mechanism, contaminated region of the air discharge port said unsaturated flame permeability aquifer to the press-fitting tube which is embedded so as to be positioned, characterized in that it is composed of an air compressor which is connected to the piezoelectric pipe through the air tank.

本発明に係る難透気透水性汚染土壌の浄化システムは、地下水位より上に存在する不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に埋設され駆動操作によって前記汚染領域内の土粒子に振動を付与する振動体と、該汚染領域に圧入され又は自然流入した空気に連行された汚染物質を該空気とともに該汚染領域の上方に設けた吸引管により吸引し浄化処理を行うガス処理設備とを備えたものであって、前記ガス処理設備を、前記不飽和難透気透水層又はその上方に拡がる不飽和透気層に埋設された吸引管と、該吸引管に接続された気液分離槽と、該気液分離槽の気相空間に連通接続された吸引ブロアと、該吸引ブロアに接続された有害物質除去装置と、前記気液分離槽の液相空間に連通接続された水処理設備とから構成したことを特徴とするThe system for purifying hardly permeable and air permeable contaminated soil according to the present invention includes the unsaturated hardly permeable and air permeable layer existing above the groundwater level, embedded in a contaminated area contaminated with a contaminant and driven by the operation. A vibrating body that imparts vibrations to the soil particles in the region, and a contaminant that is entrained in the air that is press-fitted into the contaminated region or that naturally flows into the region, is sucked together with the air by a suction pipe provided above the contaminated region, and is purified. be those with a gas treatment facility for performing the gas processing facilities, the suction tube which is embedded in the unsaturated flame permeability aquifer or unsaturated permeability layer extending thereabove, to the suction pipe A connected gas-liquid separation tank; a suction blower connected to the gas-phase space of the gas-liquid separation tank; a harmful substance removal device connected to the suction blower; and a liquid-phase space of the gas-liquid separation tank this was composed of a communication connection to the water treatment facility The features.

また、本発明に係る難透気透水性汚染土壌の浄化システムは、前記振動体を、下端が前記汚染領域に埋設される杭又は矢板と、該杭又は矢板の上端に取り付けられるバイブロハンマーとで構成したものである。   Further, in the purification system for hardly permeable and air permeable contaminated soil according to the present invention, the vibrator is composed of a pile or a sheet pile whose lower end is embedded in the contaminated area, and a vibro hammer attached to the upper end of the pile or sheet pile. It is composed.

また、本発明に係る難透気透水性汚染土壌の浄化システムは、前記振動体をバイブレータで構成したものである。   Moreover, the purification system of the hardly permeable and air permeable contaminated soil according to the present invention is configured such that the vibrator is configured by a vibrator.

本発明に係る難透気透水性汚染土壌の浄化方法及びシステムにおいては、不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に振動体を埋設し、該振動体の駆動操作によって汚染領域内の土粒子に振動を付与するとともに、該汚染領域に空気を強制圧入し又は自然流入させる。   In the purification method and system for hardly permeable and air permeable contaminated soil according to the present invention, a vibrating body is buried in a contaminated area contaminated with a contaminant in the unsaturated permeable and air permeable layer, and the vibrator is driven. The operation imparts vibration to the soil particles in the contaminated area, and air is forced into the contaminated area or naturally flows into the contaminated area.

このように土粒子に振動が付与されると、従来行われていたエアスパージング法や気泡連行浄化法とは異なり、不飽和難透気透水層の汚染領域内における土粒子同士がぶつかり合って該土粒子間にあらたな間隙が生じたり、元の大きさよりも間隙が大きくなったり、土粒子の骨格が破壊されたりするとともに、土粒子同士が擦れ合うことで該土粒子の表面に付着していた汚染物質が該表面から剥がれる。   When vibration is applied to the soil particles in this way, unlike the conventional air sparging method and bubble entrainment purification method, the soil particles collide with each other in the contaminated region of the unsaturated hardly permeable air permeable layer and the soil particles collide with each other. A new gap was created between the soil particles, the gap was larger than the original size, the skeleton of the soil particles was destroyed, and the soil particles rubbed against each other and adhered to the surface of the soil particles. Contaminants are stripped from the surface.

かかる状態においては、圧入され又は自然流入した空気が土粒子間の間隙を流れる際、その流動抵抗は大幅に低下するとともに、土粒子に付着していた汚染物質が土粒子間の間隙に遊離してくるため、汚染物質も空気に連行されやすくなる。   In such a state, when air that is injected or naturally flows through the gaps between the soil particles, the flow resistance is greatly reduced, and contaminants attached to the soil particles are released into the gaps between the soil particles. As a result, pollutants are easily taken to the air.

そのため、圧入され又は自然流入した空気に汚染物質を連行させながら、汚染物質を空気とともにガス処理設備で吸引し浄化処理を行うようにすれば、従来のエアスパージング法等では不可能だった難透気透水性汚染土壌の浄化を確実かつ効率よく行うことが可能となる。   For this reason, if the contaminants are taken into the air that has been injected or naturally flowed in, and the contaminants are sucked together with the air in the gas treatment facility to perform the purification treatment, it is difficult to achieve the difficulty of the conventional air sparging method. It becomes possible to reliably and efficiently purify the air-permeable contaminated soil.

汚染物質は、主として油や揮発性有機化合物(揮発性有機塩素化合物を含む)が対象となるが、ダイオキシン類など、空気連行可能な物質であればすべて本発明でいうところの汚染物質に含まれる。   Contaminants mainly include oil and volatile organic compounds (including volatile organic chlorine compounds), but any substance that can be air-entrained, such as dioxins, is included in the contaminants referred to in the present invention. .

不飽和難透気透水層でいう難透気透水層とは、主としてシルト層や粘土層を意味するが、透気性及び透水性が悪いために通水洗浄、ガス吸引、エアスパージング法等の従来法では汚染物質を回収することができないのであれば、シルト又は粘土のほかに砂を含む土層も当然本発明でいう難透気透水層に含まれる。   The hardly permeable air permeable layer in the unsaturated permeable air permeable layer mainly means a silt layer or a clay layer, but because of poor air permeability and water permeability, conventional methods such as water washing, gas suction, air sparging method, etc. If the pollutant cannot be recovered by the law, a soil layer containing sand in addition to silt or clay is naturally included in the hardly permeable air permeable layer referred to in the present invention.

汚染流域に空気を強制圧入させるか自然流入させるかは、不飽和難透気透水層の深さ等を考慮して適宜定めればよいが、強制圧入が必要な場合、前記汚染領域に空気を圧入する空気圧入機構を備えるとともに、該空気圧入機構を、空気吐出口が前記不飽和難透気透水層の汚染領域に位置するように埋設される圧入管と、空気タンクを介して該圧入管に接続されたエアコンプレッサーとから構成することが考えられる。   Whether forced intrusion or natural inflow of air into the contaminated basin may be appropriately determined in consideration of the depth of the unsaturated hardly permeable air permeable layer, etc. A press-fitting pipe provided with an air-fitting mechanism for press-fitting, the press-fitting pipe embedded in such a manner that an air discharge port is located in a contaminated region of the unsaturated hardly permeable air permeable layer, and the press-fitting pipe through an air tank It is conceivable that the air compressor is connected to the air compressor.

ガス処理設備の構成についても任意であるが、例えば、前記ガス処理設備を、前記不飽和難透気透水層又はその上方に拡がる不飽和透気層に埋設された吸引管と、該吸引管に接続された気液分離槽と、該気液分離槽の気相空間に連通接続された吸引ブロアと、該吸引ブロアに接続された有害物質除去装置と、前記気液分離槽の液相空間に連通接続された水処理設備とから構成することが考えられる。   Although the configuration of the gas treatment facility is also arbitrary, for example, the gas treatment facility includes a suction pipe embedded in the unsaturated hardly permeable air permeable layer or the unsaturated air permeable layer extending above, and the suction pipe. A connected gas-liquid separation tank; a suction blower connected to the gas-phase space of the gas-liquid separation tank; a harmful substance removal device connected to the suction blower; and a liquid-phase space of the gas-liquid separation tank It is conceivable to configure a water treatment facility connected in communication.

吸引管の配置形態としては、不飽和難透気透水層が深い場合、該不飽和難透気透水層の上方に拡がる不飽和透気層に水平に埋設する形態や、逆に不飽和難透気透水層が浅い場合には、不飽和難透気透水層に貫入されるボーリング孔を地上から鉛直に掘削し、該ボーリング孔に吸引管を挿入配置する形態が考えられる。   As the arrangement form of the suction pipe, when the unsaturated hardly permeable permeable layer is deep, the suction pipe is horizontally embedded in the unsaturated permeable layer extending above the unsaturated hardly permeable permeable layer, or conversely, the unsaturated hardly permeable permeable layer. In the case where the air permeable layer is shallow, a form in which a borehole penetrating into the unsaturated hardly permeable air permeable layer is excavated vertically from the ground, and a suction pipe is inserted and disposed in the borehole is conceivable.

上述した発明において、振動体は、不飽和難透気透水層における汚染領域内の土粒子を振動させることができるのであれば、どのような構成でもかまわないが、例えば、前記振動体を、下端が前記汚染領域に埋設される杭又は矢板と、該杭又は矢板の上端に取り付けられるバイブロハンマーとで構成する、あるいは、バイブレータで構成することが考えられる。   In the above-described invention, the vibrating body may have any configuration as long as it can vibrate the soil particles in the contaminated region in the unsaturated hardly permeable air permeable layer. May be constituted by a pile or sheet pile embedded in the contaminated area and a vibro hammer attached to the upper end of the pile or sheet pile, or may be constituted by a vibrator.

なお、本出願人は、振動体によって土粒子を振動させ、それによって上述した作用を生ぜしめ、ひいては難透気透水層の透気性を改善することができることを新規に見いだしたものであり、産業上きわめて有用な知見であるとともに、従来技術に比して顕著な作用効果を有することを付言しておく。   The present applicant has newly found that the soil particles can be vibrated by a vibrating body, thereby causing the above-described action, and thus improving the air permeability of the hardly air-permeable water-permeable layer. It should be noted that this is a very useful finding and has a remarkable effect as compared with the prior art.

以下、本発明に係る難透気透水性汚染土壌の浄化方法及びシステムの実施の形態について、添付図面を参照して説明する。なお、従来技術と実質的に同一の部品等については同一の符号を付してその説明を省略する。   DESCRIPTION OF EMBODIMENTS Hereinafter, embodiments of a purification method and system for hardly permeable and air permeable contaminated soil according to the present invention will be described with reference to the accompanying drawings. Note that components that are substantially the same as those of the prior art are assigned the same reference numerals, and descriptions thereof are omitted.

(第1実施形態) (First embodiment)

図1は、本実施形態に係る難透気透水性汚染土壌の浄化システムを示した図である。本実施形態に係る難透気透水性汚染土壌の浄化システム1は同図に示すように、振動体としての鋼製矢板20及び該鋼製矢板の上端に取り付けられたバイブロハンマー10と、飽和層6に位置する地下水位より上に存在する不飽和難透気透水層2のうち、油やダイオキシン類あるいは揮発性有機塩素化合物といった汚染物質3で汚染されている汚染領域4に空気を強制的に圧入する空気圧入機構5と、圧入された空気が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気とともに吸引し浄化処理を行うガス処理設備13とを備え、鋼製矢板20は、その下端を不飽和難透気透水層2の汚染領域4に埋設してあり、バイブロハンマー10を駆動操作することによって、汚染領域4内の土粒子に振動を付与することができるようになっている。   FIG. 1 is a view showing a purification system for hardly air permeable and contaminated soil according to the present embodiment. As shown in the figure, the hardly permeable and air permeable contaminated soil purification system 1 according to the present embodiment includes a steel sheet pile 20 as a vibrating body, a vibro hammer 10 attached to the upper end of the steel sheet pile, and a saturated layer. Forcing air into the contaminated area 4 contaminated with the pollutant 3 such as oil, dioxins or volatile organic chlorine compounds in the unsaturated hardly permeable air permeable layer 2 existing above the groundwater level located at 6 An air pressure injection mechanism 5 for press-fitting and a gas processing facility 13 for performing a purification process by sucking the pollutant 3 together with the air after the pressurized air ascends the unsaturated air permeable layer 7 while entraining the pollutant 3. The lower end of the steel sheet pile 20 is embedded in the contaminated region 4 of the unsaturated hardly permeable air permeable layer 2, and the vibration is imparted to the soil particles in the contaminated region 4 by driving the vibro hammer 10. It is possible It has become way.

不飽和難透気透水層2は、シルト、粘土又は粘性土を主成分とする土からなるため、透気性及び透水性に劣り、そのままの状態では通水洗浄やガス吸引が困難な土層であり、それに対し、不飽和透気層7は、透気性を有する例えば砂質土からなる土層となっている。   Unsaturated hardly permeable air permeable layer 2 is made of soil mainly composed of silt, clay, or clay soil, and is poor in air permeability and water permeability. On the other hand, the unsaturated air permeable layer 7 is a soil layer made of sandy soil having air permeability.

空気圧入機構5は、エアコンプレッサー12と、該エアコンプレッサーから送気されてきた空気を中間貯留する空気タンク11と、該空気タンク11に接続され空気吐出口8が不飽和難透気透水層2の汚染領域4に位置するように埋設される圧入管9とから構成してあり、エアコンプレッサー12からの空気を圧入管9を介して汚染領域4に圧入することができるようになっている。   The air pressure input mechanism 5 includes an air compressor 12, an air tank 11 that intermediately stores the air supplied from the air compressor, and an air discharge port 8 connected to the air tank 11 with an unsaturated hardly air permeable water-permeable layer 2. The press-in pipe 9 is embedded so as to be located in the contaminated area 4, and air from the air compressor 12 can be press-fitted into the contaminated area 4 through the press-in pipe 9.

ガス処理設備13は、不飽和難透気透水層2の上方に拡がる不飽和透気層7に埋設された吸引管14と、該吸引管に接続された気液分離槽15と、該気液分離槽の気相空間に連通接続された吸引ブロア16と、該吸引ブロアに接続された有害物質除去装置としての活性炭フィルター槽17と、気液分離槽の液相空間に連通接続された水処理設備18とから構成してある。   The gas treatment facility 13 includes a suction pipe 14 embedded in the unsaturated gas permeable layer 7 extending above the unsaturated hardly gas permeable water layer 2, a gas-liquid separation tank 15 connected to the suction pipe, and the gas liquid A suction blower 16 communicatively connected to the gas phase space of the separation tank, an activated carbon filter tank 17 as a harmful substance removal device connected to the suction blower, and a water treatment communicatively connected to the liquid phase space of the gas-liquid separation tank It is composed of equipment 18.

本実施形態に係る難透気透水性汚染土壌の浄化システム1を設置するには、まず、不飽和難透気透水層2のうち、汚染物質で汚染されている汚染領域4に空気圧入機構5の圧入管9を建て込む。   In order to install the purification system 1 for the hardly permeable and air permeable contaminated soil according to this embodiment, first, the pneumatic injection mechanism 5 is placed in the contaminated area 4 of the unsaturated permeable and permeable water permeable layer 2 that is contaminated with the contaminant. The press-in pipe 9 is installed.

圧入管9を建て込むにあたっては、あらかじめ該当位置をボーリングし、次いで該ボーリング孔に圧入管9を挿入し、しかる後、空気吐出口8が閉塞されることがないよう、圧入管9とボーリング孔との間に所定量の砂を先行充填する一方、圧入管9を固定すべく、ボーリング孔との隙間には空気吐出口8よりも浅い箇所において、モルタル、ベントナイトなどを充填する。   When the press-fit pipe 9 is installed, the corresponding position is bored in advance, and then the press-fit pipe 9 is inserted into the bore hole, and then the press-fit pipe 9 and the bore hole are prevented so that the air discharge port 8 is not blocked. In order to fix the press-fitting pipe 9 in between, a mortar, bentonite, etc. are filled in a space shallower than the air discharge port 8 in order to fix the press-fitting pipe 9.

次に、圧入管9の上端に空気タンク11及びエアコンプレッサー12を順次接続する。   Next, an air tank 11 and an air compressor 12 are sequentially connected to the upper end of the press-fit pipe 9.

かかる圧入管9の建込みと相前後して、不飽和透気層7に貫入するように鋼製矢板20を打ち込み、その下端を不飽和難透気透水層2のうち、汚染物質で汚染されている汚染領域4に埋設し、次いで、鋼製矢板20の上端にバイブロハンマー10を取り付ける。なお、鋼製矢板20の打込みをバイブロハンマー10で行うようにしてもよい。   The steel sheet pile 20 is driven so as to penetrate into the unsaturated gas permeable layer 7 before and after the installation of the press-fitting pipe 9, and the lower end thereof is contaminated with the pollutant in the unsaturated gas permeable layer 2. The vibro hammer 10 is attached to the upper end of the steel sheet pile 20. The steel sheet pile 20 may be driven with the vibro hammer 10.

一方、不飽和透気層7に吸引管14を埋設するとともに該吸引管に気液分離装置15を接続し、しかる後、上述したようにその気相空間に連通するように吸引ブロア16及び活性炭フィルター槽17を順次接続するとともに、その液相空間に連通するように水処理設備18を接続する。   On the other hand, a suction pipe 14 is embedded in the unsaturated gas permeable layer 7 and a gas-liquid separation device 15 is connected to the suction pipe. Thereafter, as described above, the suction blower 16 and activated carbon are communicated with the gas phase space. The filter tank 17 is sequentially connected, and the water treatment facility 18 is connected so as to communicate with the liquid phase space.

このように設置された浄化システム1を用いて難透気透水性汚染土壌、本実施形態では不飽和難透気透水層2の汚染領域4を浄化するには、まず、バイブロハンマー10を駆動操作することにより、鋼製矢板20を介して汚染領域4内の土粒子に振動を付与するとともに、エアコンプレッサー12、空気タンク11及び圧力容器10を適宜作動させることで不飽和難透気透水層2の汚染領域4に空気を圧入する。   In order to purify the hardly permeable and air permeable contaminated soil, in this embodiment, the contaminated region 4 of the unsaturated permeable and permeable water permeable layer 2 using the purification system 1 installed in this way, first, the drive operation of the vibro hammer 10 is performed. Thus, vibration is imparted to the soil particles in the contaminated region 4 through the steel sheet pile 20, and the air compressor 12, the air tank 11, and the pressure vessel 10 are operated as appropriate so that the unsaturated hardly permeable air permeable layer 2. Air is injected into the contaminated area 4 of the air.

このようにすると、従来行われていたエアスパージング法や気泡連行浄化法とは異なり、鋼製矢板20を介したバイブロハンマー10による振動付与により、不飽和難透気透水層2の汚染領域4内における土粒子同士がぶつかり合って該土粒子間にあらたな間隙が生じたり、元の大きさよりも間隙が大きくなったり、粘性土の骨格が破壊されたりするとともに、土粒子同士が擦れ合うことで該土粒子の表面に付着していた汚染物質が該表面から剥がれる。   In this case, unlike the conventionally performed air sparging method and bubble entrainment purification method, vibration is imparted by the vibro hammer 10 through the steel sheet pile 20, so that in the contaminated region 4 of the unsaturated hardly permeable air permeable layer 2. The soil particles collide with each other to form a new gap between the soil particles, the gap becomes larger than the original size, the skeleton of the viscous soil is destroyed, and the soil particles rub against each other. Contaminants attached to the surface of the soil particles are peeled off from the surface.

図2は、それらのうち、粘性土の骨格破壊が生じる場合を例に挙げたものであって、同図(a)はバイブロハンマー10の駆動操作を行う前の粘性土の骨格、同図(b)はかかる駆動操作を行った後の粘性土の骨格の様子を模式的に示したものである。   FIG. 2 shows an example of the case where the skeletal fracture of the viscous soil occurs, and FIG. 2A shows the skeleton of the viscous soil before the driving operation of the vibro hammer 10. b) schematically shows the skeleton of the cohesive soil after such a driving operation.

これらの図でわかるように、粘性土の骨格は、バイブロハンマー10の駆動操作により破壊されて土粒子がばらばらになり、空隙21があらたに生じるとともに、土粒子表面に付着していた汚染物質3は該土粒子から剥離する。   As can be seen from these figures, the skeleton of the viscous soil is broken by the driving operation of the vibro hammer 10 so that the soil particles are separated, the voids 21 are newly formed, and the contaminant 3 attached to the surface of the soil particles 3 Peels from the soil particles.

骨格が破壊されない場合も、バイブロハンマー10の駆動操作によってあらたな間隙が生じたり、元の間隙が大きくなったりすることに変わりはなく、かくして、圧入管9を介して圧入された空気22は、土粒子間の間隙21を流れる際、その流動抵抗が大幅に低下して流れやすくなるとともに、土粒子に付着していた汚染物質3が土粒子間の間隙21に遊離しているため、汚染物質3も空気22に連行されやすくなる。   Even when the skeleton is not destroyed, a new gap is generated by the driving operation of the vibro hammer 10 or the original gap is increased. Thus, the air 22 press-fitted through the press-fitting pipe 9 is When flowing through the gaps 21 between the soil particles, the flow resistance is greatly lowered and the flow is facilitated, and the contaminant 3 adhering to the soil particles is released in the gaps 21 between the soil particles. 3 is also easily taken to the air 22.

次に、圧入された空気22が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気22とともにガス処理設備13で吸引し浄化処理を行う。吸引は、吸引ブロア16を作動させることにより行う。   Next, after the pressurized air 22 moves up the unsaturated air permeable layer 7 while entraining the pollutant 3, the pollutant 3 is sucked together with the air 22 by the gas treatment facility 13 to perform a purification process. Suction is performed by operating the suction blower 16.

次に、吸引された汚染物質連行空気を気液分離槽15で液体と気体に分離し、気体については、活性炭フィルター槽17に通して汚染物質3を活性炭に吸着させ、その後、大気に放出するとともに、液体については、水処理設備18で汚染物質3を除去し、その後、河川等に放流する。   Next, the sucked pollutant entrained air is separated into liquid and gas in the gas-liquid separation tank 15, and the gas is passed through the activated carbon filter tank 17 to adsorb the pollutant 3 on the activated carbon, and then released to the atmosphere. At the same time, for the liquid, the pollutant 3 is removed by the water treatment facility 18 and then discharged into a river or the like.

なお、不飽和透気層7といえども、吸引される物質は完全にガスだけではなく、降雨等の気象条件によっては多少なりとも水分も吸引されるため、気液分離槽15を介在させるとともに水処理設備18を設置するのが望ましいことは言うまでもない。   Even in the case of the unsaturated air permeable layer 7, the substance to be sucked is not only gas but also moisture is sucked in some amounts depending on weather conditions such as rainfall, and therefore the gas-liquid separation tank 15 is interposed. Needless to say, it is desirable to install the water treatment facility 18.

以上説明したように、本実施形態に係る難透気透水性汚染土壌の浄化方法及びシステムによれば、従来行われていたエアスパージング法や気泡連行浄化法とは異なり、鋼製矢板20を介したバイブロハンマー10による汚染領域4への振動付与により、土粒子同士がぶつかり合って該土粒子間にあらたな間隙が生じたり、元の大きさよりも間隙が大きくなったり、土粒子の骨格が破壊されたりするとともに、土粒子同士が擦れ合うことで該土粒子の表面に付着していた汚染物質3が該表面から剥がれる。   As described above, according to the purification method and system for hardly permeable and air permeable contaminated soil according to the present embodiment, unlike the conventional air sparging method and bubble entrainment purification method, the steel sheet pile 20 is interposed. By applying vibration to the contaminated area 4 by the vibro hammer 10, the soil particles collide with each other to create a new gap between the soil particles, the gap becomes larger than the original size, or the soil particle skeleton is destroyed. At the same time, the soil particles rub against each other, so that the contaminant 3 attached to the surface of the soil particles is peeled off from the surface.

かかる状態においては、圧入された空気22が土粒子間の間隙を流れる際、その流動抵抗は大幅に低下するとともに、土粒子に付着していた汚染物質3が土粒子間の間隙に遊離してくるため、汚染物質3も空気22に連行されやすくなる。   In such a state, when the injected air 22 flows through the gap between the soil particles, the flow resistance is greatly reduced, and the contaminant 3 attached to the soil particles is released into the gap between the soil particles. Therefore, the contaminant 3 is also easily taken to the air 22.

そのため、圧入された空気22が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気22とともに吸引し浄化処理を行うようにすれば、従来のエアスパージング法等では不可能だった不飽和難透気透水層2の浄化を確実かつ効率よく行うことが可能となる。   For this reason, if the injected air 22 moves up the unsaturated air permeable layer 7 while entraining the pollutant 3, and then purifies the pollutant 3 together with the air 22, a conventional air sparging method, etc. Then, it becomes possible to reliably and efficiently purify the unsaturated hardly permeable air permeable layer 2 that was impossible.

本実施形態では、バイブロハンマー10の加振力を汚染領域4に伝達させる部材として鋼製矢板20を採用したが、汚染領域4内の土粒子に振動を付与することができるのであれば、どのような部材でもかまわない。例えば、鋼製矢板20に代えて杭を使用することが可能である。   In the present embodiment, the steel sheet pile 20 is employed as a member that transmits the excitation force of the vibro hammer 10 to the contaminated region 4. However, any material can be used as long as vibration can be imparted to the soil particles in the contaminated region 4. Such a member may be used. For example, a pile can be used instead of the steel sheet pile 20.

また、本実施形態では、空気圧入機構5を用いて不飽和難透気透水層2の汚染領域4に強制的に空気を圧入するようにしたが、例えば不飽和難透気透水層2が比較的浅いために空気を強制的に圧入せずとも、地表面から不飽和透気層7を介して汚染領域4に自然流入させることができるのであれば、空気圧入機構5を省略してもかまわない。   In the present embodiment, air is forcibly injected into the contaminated region 4 of the unsaturated hardly permeable air permeable layer 2 using the pneumatic insertion mechanism 5, but for example, the unsaturated hardly permeable air permeable layer 2 is compared. If the air can be naturally introduced from the ground surface into the contaminated area 4 via the unsaturated air permeable layer 7 without forcedly injecting the air due to the shallowness, the air pressure input mechanism 5 may be omitted. Absent.

(第2実施形態) (Second Embodiment)

次に、第2実施形態について説明する。なお、上述の実施形態と実質的に同一の部品等については同一の符号を付してその説明を省略する。   Next, a second embodiment will be described. Note that components that are substantially the same as those of the above-described embodiment are denoted by the same reference numerals, and description thereof is omitted.

図3は、第2実施形態に係る難透気透水性汚染土壌の浄化システムを示した図である。本実施形態に係る難透気透水性汚染土壌の浄化システム41は同図に示すように、振動体としてのバイブレータ42と、飽和層6に位置する地下水位より上に存在する不飽和難透気透水層2のうち、油やダイオキシン類あるいは揮発性有機塩素化合物といった汚染物質3で汚染されている汚染領域4に空気を強制的に圧入する空気圧入機構5と、圧入された空気が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気とともに吸引し浄化処理を行うガス処理設備13とを備え、バイブレータ42は、不飽和難透気透水層2の汚染領域4に埋設してあり、該バイブレータを駆動操作することによって、汚染領域4内の土粒子に振動を付与することができるようになっている。   FIG. 3 is a diagram showing a purification system for hardly air permeable and contaminated soil according to the second embodiment. As shown in the figure, the hardly permeable and air permeable contaminated soil purification system 41 according to the present embodiment includes a vibrator 42 as a vibrating body and an unsaturated permeable air that exists above the groundwater level located in the saturated layer 6. Of the water permeable layer 2, an air pressure injection mechanism 5 for forcibly injecting air into a polluted area 4 contaminated with a pollutant 3 such as oil, dioxins or volatile organic chlorine compounds, and the injected air is pollutant 3. And the gas treatment equipment 13 that performs the purification process by sucking the pollutant 3 together with air after the unsaturated air-permeable layer 7 is lifted, and the vibrator 42 is a contaminated region of the unsaturated air-permeable layer 2 4, and the vibration can be applied to the soil particles in the contaminated region 4 by driving the vibrator.

不飽和難透気透水層2は、シルト、粘土又は粘性土を主成分とする土からなるため、透気性及び透水性に劣り、そのままの状態では通水洗浄やガス吸引が困難な土層であり、それに対し、不飽和透気層7は、透気性を有する例えば砂質土からなる土層となっている。   Unsaturated hardly permeable air permeable layer 2 is made of soil mainly composed of silt, clay, or clay soil, and is poor in air permeability and water permeability. On the other hand, the unsaturated air permeable layer 7 is a soil layer made of sandy soil having air permeability.

本実施形態に係る難透気透水性汚染土壌の浄化システム41を設置するには、まず、不飽和難透気透水層2のうち、汚染物質で汚染されている汚染領域4に空気圧入機構5の圧入管9を建て込む。   In order to install the purification system 41 for the hardly permeable and air permeable contaminated soil according to the present embodiment, first, the pneumatic injection mechanism 5 is placed in the contaminated region 4 of the unsaturated permeable and air permeable layer 2 that is contaminated with the contaminant. The press-in pipe 9 is installed.

圧入管9を建て込むにあたっては、あらかじめ該当位置をボーリングし、次いで該ボーリング孔に圧入管9を挿入し、しかる後、空気吐出口8が閉塞されることがないよう、圧入管9とボーリング孔との間に所定量の砂を先行充填する一方、圧入管9を固定すべく、ボーリング孔との隙間には空気吐出口8よりも浅い箇所において、モルタル、ベントナイトなどを充填する。   When the press-fit pipe 9 is installed, the corresponding position is bored in advance, and then the press-fit pipe 9 is inserted into the bore hole, and then the press-fit pipe 9 and the bore hole are prevented so that the air discharge port 8 is not blocked. In order to fix the press-fitting pipe 9 in between, a mortar, bentonite, etc. are filled in a space shallower than the air discharge port 8 in order to fix the press-fitting pipe 9.

次に、圧入管9の上端に空気タンク11及びエアコンプレッサー12を順次接続する。   Next, an air tank 11 and an air compressor 12 are sequentially connected to the upper end of the press-fit pipe 9.

かかる圧入管9の建込みと相前後して、不飽和難透気透水層2のうち、汚染物質で汚染されている汚染領域4にバイブレータ42を適宜数埋設し、該各バイブレータを図示しない電源装置に接続する。   Before and after the installation of the press-fitting pipe 9, an appropriate number of vibrators 42 are buried in the contaminated region 4 contaminated with the pollutant in the unsaturated hardly permeable air permeable layer 2, and the vibrators are not shown. Connect to the device.

一方、不飽和透気層7に吸引管14を埋設するとともに該吸引管に気液分離装置15を接続し、しかる後、上述したようにその気相空間に連通するように吸引ブロア16及び活性炭フィルター槽17を順次接続するとともに、その液相空間に連通するように水処理設備18を接続する。   On the other hand, a suction pipe 14 is embedded in the unsaturated gas permeable layer 7 and a gas-liquid separation device 15 is connected to the suction pipe. Thereafter, as described above, the suction blower 16 and activated carbon are communicated with the gas phase space. The filter tank 17 is sequentially connected, and the water treatment facility 18 is connected so as to communicate with the liquid phase space.

このように設置された浄化システム41を用いて難透気透水性汚染土壌、本実施形態では不飽和難透気透水層2の汚染領域4を浄化するには、まず、バイブレータ42を駆動操作することにより、汚染領域4内の土粒子に振動を付与するとともに、エアコンプレッサー12、空気タンク11及び圧力容器10を適宜作動させることで不飽和難透気透水層2の汚染領域4に空気を圧入する。   In order to purify the hardly permeable and air permeable contaminated soil, in this embodiment, the contaminated region 4 of the unsaturated permeable and permeable water permeable layer 2 using the purification system 41 thus installed, first, the vibrator 42 is driven. As a result, vibration is applied to the soil particles in the contaminated area 4 and air is pressed into the contaminated area 4 of the unsaturated hardly permeable air permeable layer 2 by appropriately operating the air compressor 12, the air tank 11 and the pressure vessel 10. To do.

このようにすると、従来行われていたエアスパージング法や気泡連行浄化法とは異なり、バイブレータ42による汚染領域4への振動付与により、不飽和難透気透水層2の汚染領域4内における土粒子同士がぶつかり合って該土粒子間にあらたな間隙が生じたり、元の大きさよりも間隙が大きくなったり、粘性土の骨格が破壊されたりするとともに、土粒子同士が擦れ合うことで該土粒子の表面に付着していた汚染物質が該表面から剥がれる。   In this way, unlike the conventional air sparging method and bubble entrainment purification method, by applying vibration to the contaminated region 4 by the vibrator 42, soil particles in the contaminated region 4 of the unsaturated hardly permeable air permeable layer 2 are provided. The soil particles collide with each other to create a new gap between the soil particles, the gap becomes larger than the original size, the skeleton of the viscous soil is destroyed, and the soil particles rub against each other. Contaminants adhering to the surface are peeled off from the surface.

例えば、粘性土の骨格は、バイブレータ42の駆動操作により破壊されて土粒子がばらばらになり、空隙があらたに生じるとともに、土粒子表面に付着していた汚染物質3は該土粒子から剥離する。   For example, the skeleton of the viscous soil is broken by the driving operation of the vibrator 42, and the soil particles are separated, voids are newly generated, and the contaminant 3 attached to the surface of the soil particles is separated from the soil particles.

骨格が破壊されない場合も、バイブレータ42の駆動操作によってあらたな間隙が生じたり、元の間隙が大きくなったりすることに変わりはなく、かくして、圧入管9を介して圧入された空気は、土粒子間の間隙を流れる際、その流動抵抗が大幅に低下して流れやすくなるとともに、土粒子に付着していた汚染物質3が土粒子間の間隙に遊離しているため、汚染物質3も空気に連行されやすくなる。   Even when the skeleton is not destroyed, a new gap is generated by the driving operation of the vibrator 42, or the original gap is increased, and thus the air press-fitted through the press-fitting pipe 9 becomes soil particles. When flowing through the gaps between them, the flow resistance is greatly reduced and the flow is facilitated, and the contaminants 3 adhering to the soil particles are released in the gaps between the soil particles. It becomes easy to be taken.

次に、圧入された空気が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気とともにガス処理設備13で吸引し浄化処理を行う。吸引は、吸引ブロア16を作動させることにより行う。   Next, after the injected air moves up the unsaturated air permeable layer 7 while entraining the pollutant 3, the pollutant 3 is sucked together with the air by the gas treatment facility 13 to perform a purification process. Suction is performed by operating the suction blower 16.

次に、吸引された汚染物質連行空気を気液分離槽15で液体と気体に分離し、気体については、活性炭フィルター槽17に通して汚染物質3を活性炭に吸着させ、その後、大気に放出するとともに、液体については、水処理設備18で汚染物質3を除去し、その後、河川等に放流する。   Next, the sucked pollutant entrained air is separated into liquid and gas in the gas-liquid separation tank 15, and the gas is passed through the activated carbon filter tank 17 to adsorb the pollutant 3 on the activated carbon, and then released to the atmosphere. At the same time, for the liquid, the pollutant 3 is removed by the water treatment facility 18 and then discharged into a river or the like.

なお、不飽和透気層7といえども、吸引される物質は完全にガスだけではなく、降雨等の気象条件によっては多少なりとも水分も吸引されるため、気液分離槽15を介在させるとともに水処理設備18を設置するのが望ましいことは言うまでもない。   Even in the case of the unsaturated air permeable layer 7, the substance to be sucked is not only gas but also moisture is sucked in some amounts depending on weather conditions such as rainfall, and therefore the gas-liquid separation tank 15 is interposed. Needless to say, it is desirable to install the water treatment facility 18.

以上説明したように、本実施形態に係る難透気透水性汚染土壌の浄化方法及びシステムによれば、従来行われていたエアスパージング法や気泡連行浄化法とは異なり、バイブレータ42による汚染領域4への振動付与により、土粒子同士がぶつかり合って該土粒子間にあらたな間隙が生じたり、元の大きさよりも間隙が大きくなったり、土粒子の骨格が破壊されたりするとともに、土粒子同士が擦れ合うことで該土粒子の表面に付着していた汚染物質3が該表面から剥がれる。   As described above, according to the purification method and system for hardly permeable and air permeable contaminated soil according to the present embodiment, the contaminated region 4 due to the vibrator 42 is different from the conventional air sparging method and bubble entrainment purification method. By applying vibration to the soil particles, the soil particles collide with each other, and a new gap is generated between the soil particles, the gap becomes larger than the original size, or the skeleton of the soil particles is destroyed. As a result of rubbing, the contaminant 3 adhering to the surface of the soil particles is peeled off from the surface.

かかる状態においては、圧入された空気が土粒子間の間隙を流れる際、その流動抵抗は大幅に低下するとともに、土粒子に付着していた汚染物質3が土粒子間の間隙に遊離してくるため、汚染物質3も空気に連行されやすくなる。   In such a state, when the injected air flows through the gaps between the soil particles, the flow resistance is greatly reduced, and the contaminant 3 attached to the soil particles is released into the gaps between the soil particles. Therefore, the contaminant 3 is also easily taken to the air.

そのため、圧入された空気が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気とともに吸引し浄化処理を行うようにすれば、従来のエアスパージング法等では不可能だった不飽和難透気透水層2の浄化を確実かつ効率よく行うことが可能となる。   For this reason, if the injected air moves up the unsaturated air permeable layer 7 while entraining the pollutant 3 and then the contaminant 3 is sucked together with the air to perform the purification process, it is not possible with the conventional air sparging method or the like. It becomes possible to reliably and efficiently purify the unsaturated hardly permeable air permeable layer 2 that has been possible.

本実施形態では、空気圧入機構5を用いて不飽和難透気透水層2の汚染領域4に強制的に空気を圧入するようにしたが、例えば不飽和難透気透水層2が比較的浅いために空気を強制的に圧入せずとも、地表面から不飽和透気層7を介して汚染領域4に自然流入させることができるのであれば、空気圧入機構5を省略してもかまわない。   In the present embodiment, air is forcibly pressed into the contaminated region 4 of the unsaturated hardly permeable air permeable layer 2 using the air pressure input mechanism 5. For example, the unsaturated hardly permeable air permeable layer 2 is relatively shallow. Therefore, the air pressure insertion mechanism 5 may be omitted as long as air can be naturally introduced from the ground surface into the contaminated region 4 through the unsaturated air permeable layer 7 without forcedly injecting air.

また、本実施形態では、吸引管14を不飽和透気層7に水平に埋設したが、不飽和難透気透水層2が浅い場合には、かかる構成に代えて、不飽和難透気透水層2に貫入されるボーリング孔を地上から適宜本数だけ鉛直に掘削し、該各ボーリング孔に吸引管を挿入配置するようにしてもよい。   Moreover, in this embodiment, although the suction pipe 14 was embed | buried horizontally in the unsaturated air permeable layer 7, when the unsaturated hardly permeable air permeable layer 2 is shallow, it replaces with this structure and is unsaturated unsaturated permeable air permeable water. An appropriate number of boreholes penetrating into the layer 2 may be excavated vertically from the ground, and suction pipes may be inserted into the respective boreholes.

このような鉛直に形成されたボーリング孔に挿入される吸引管の構成としては、例えば中空パイプの一端に吸引孔を形成するとともに該吸引孔の周りに目詰まり防止用のメッシュ材を巻き付けて構成し、該吸引孔を形成した箇所が不飽和難透気透水層2に貫入されるように吸引管を設置すればよい。   As a structure of the suction pipe inserted into such a vertically formed boring hole, for example, a suction hole is formed at one end of a hollow pipe and a mesh material for preventing clogging is wound around the suction hole. Then, the suction pipe may be installed so that the portion where the suction hole is formed penetrates into the unsaturated hardly permeable air permeable layer 2.

第1実施形態に係る難透気透水性汚染土壌の浄化システムの概略図。Schematic of the purification system of the hardly air permeable water-contaminated soil which concerns on 1st Embodiment. 第1実施形態に係る難透気透水性汚染土壌の浄化方法の作用の一例を示した模式図。The schematic diagram which showed an example of the effect | action of the purification method of the hardly air permeable permeation | contamination soil which concerns on 1st Embodiment. 第2実施形態に係る難透気透水性汚染土壌の浄化システムの概略図。Schematic of the purification system of the hardly air permeable water-contaminated soil which concerns on 2nd Embodiment.

符号の説明Explanation of symbols

1,41 難透気透水性汚染土壌の浄化システム
2 不飽和難透気透水層
3 汚染物質
4 汚染領域
5 空気圧入機構
7 不飽和透気層
9 圧入管
10 バイブロハンマー(振動体)
11 空気タンク
12 エアコンプレッサー
13 ガス処理設備
14 吸引管
15 気液分離槽
16 吸引ブロア
17 活性炭フィルター槽(有害物質除去装置)
18 水処理設備
20 鋼製矢板(振動体)
42 バイブレータ(振動体)
1,41 Purification system for poorly permeable and permeable contaminated soil 2 Unsaturated permeable and permeable layer 3 Pollutant 4 Contaminated area 5 Pneumatic insertion mechanism 7 Unsaturated permeable layer 9 Press-in pipe 10 Vibro hammer (vibrating body)
11 Air tank 12 Air compressor 13 Gas processing equipment 14 Suction pipe 15 Gas-liquid separation tank 16 Suction blower 17 Activated carbon filter tank (Toxic substance removal device)
18 Water treatment equipment 20 Steel sheet pile (vibrating body)
42 Vibrator

Claims (6)

地下水位より上に存在する不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に振動体を埋設し、該振動体の駆動操作によって前記汚染領域内の土粒子に振動を付与し、該汚染領域に圧入され又は自然流入した空気に前記汚染物質を連行させながら前記汚染物質を前記空気とともに該汚染領域の上方に設けた吸引管により吸引し浄化処理を行う難透気透水性汚染土壌の浄化方法であって、
前記振動体を、下端が前記汚染領域に埋設される杭又は矢板と、該杭又は矢板の上端に取り付けられるバイブロハンマーとで構成したことを特徴とする難透気透水性汚染土壌の浄化方法。
A vibration body is embedded in a contaminated area contaminated with a pollutant in the unsaturated hardly permeable air permeation layer that exists above the groundwater level, and the soil particles in the contaminated area are vibrated by driving the vibration body. Impervious air permeation for giving a purification process by sucking the contaminants together with the air with a suction pipe provided above the contaminated area while entraining the pollutant into the air that is press-fitted into the contaminated area or naturally flows in A method for remediation of toxic soil,
A method for purifying hardly air-permeable and permeable contaminated soil, characterized in that the vibrator is composed of a pile or sheet pile whose lower end is buried in the contaminated area, and a vibro hammer attached to the upper end of the pile or sheet pile.
地下水位より上に存在する不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に振動体を埋設し、該振動体の駆動操作によって前記汚染領域内の土粒子に振動を付与し、該汚染領域に圧入され又は自然流入した空気に前記汚染物質を連行させながら前記汚染物質を前記空気とともに該汚染領域の上方に設けた吸引管により吸引し浄化処理を行う難透気透水性汚染土壌の浄化方法であって、
前記振動体をバイブレータで構成したことを特徴とする難透気透水性汚染土壌の浄化方法。
A vibration body is embedded in a contaminated area contaminated with a pollutant in the unsaturated hardly permeable air permeation layer that exists above the groundwater level, and the soil particles in the contaminated area are vibrated by driving the vibration body. Impervious air permeation for giving a purification process by sucking the contaminants together with the air with a suction pipe provided above the contaminated area while entraining the pollutant into the air that is press-fitted into the contaminated area or naturally flows in A method for remediation of toxic soil,
A method for purifying hardly air-permeable and water-contaminated soil, wherein the vibrator is composed of a vibrator.
地下水位より上に存在する不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に埋設され駆動操作によって前記汚染領域内の土粒子に振動を付与する振動体と、該汚染領域に圧入され又は自然流入した空気に連行された汚染物質を該空気とともに該汚染領域の上方に設けた吸引管により吸引し浄化処理を行うガス処理設備とを備えた難透気透水性汚染土壌の浄化システムであって、
前記汚染領域に空気を圧入する空気圧入機構を備えるとともに、該空気圧入機構を、空気吐出口が前記不飽和難透気透水層の汚染領域に位置するように埋設される圧入管と、空気タンクを介して該圧入管に接続されたエアコンプレッサーとから構成したことを特徴とする難透気透水性汚染土壌の浄化システム。
Of the unsaturated hardly permeable air permeable layer existing above the groundwater level, the vibrator is embedded in a contaminated area contaminated with a contaminant and imparts vibration to soil particles in the contaminated area by a driving operation, and the contamination Non-breathable water-permeable contaminated soil comprising a gas treatment facility that performs a purification process by sucking a contaminant introduced into the area or naturally entrained air with a suction pipe provided above the contaminated area Purification system,
An air injection mechanism that pressurizes air into the contaminated area, and the air injection mechanism includes a press-fit pipe embedded in an air discharge port located in the contaminated area of the unsaturated hardly permeable air permeable layer; and an air tank A system for purifying hardly air-permeable and permeable contaminated soil, comprising an air compressor connected to the press-fitting pipe via
地下水位より上に存在する不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に埋設され駆動操作によって前記汚染領域内の土粒子に振動を付与する振動体と、該汚染領域に圧入され又は自然流入した空気に連行された汚染物質を該空気とともに該汚染領域の上方に設けた吸引管により吸引し浄化処理を行うガス処理設備とを備えた難透気透水性汚染土壌の浄化システムであって、
前記ガス処理設備を、前記不飽和難透気透水層又はその上方に拡がる不飽和透気層に埋設された吸引管と、該吸引管に接続された気液分離槽と、該気液分離槽の気相空間に連通接続された吸引ブロアと、該吸引ブロアに接続された有害物質除去装置と、前記気液分離槽の液相空間に連通接続された水処理設備とから構成したことを特徴とする難透気透水性汚染土壌の浄化システム。
Of the unsaturated hardly permeable air permeable layer existing above the groundwater level, the vibrator is embedded in a contaminated area contaminated with a contaminant and imparts vibration to soil particles in the contaminated area by a driving operation, and the contamination Non-breathable water-permeable contaminated soil comprising gas treatment equipment that performs a purification process by sucking a pollutant entrained in air that is press-fitted into the area or naturally flowing into the area with a suction pipe provided above the contaminated area Purification system,
A suction pipe embedded in the unsaturated hardly permeable air permeable layer or the unsaturated air permeable layer extending thereabove, a gas-liquid separation tank connected to the suction pipe, and the gas-liquid separation tank features of a suction blower, which is communicatively connected to the gas-phase space, and removing harmful substances device connected to the suction blower, by being configured and a connecting stub water treatment facility in the liquid phase space of the gas-liquid separation tank A system for purifying poorly air permeable and contaminated soil.
前記振動体を、下端が前記汚染領域に埋設される杭又は矢板と、該杭又は矢板の上端に取り付けられるバイブロハンマーとで構成した請求項3又は4に記載の難透気透水性汚染土壌の浄化システム。 5. The hardly permeable and air permeable contaminated soil according to claim 3 , wherein the vibrating body is composed of a pile or a sheet pile whose lower end is embedded in the contaminated area and a vibro hammer attached to the upper end of the pile or sheet pile. Purification system. 前記振動体をバイブレータで構成した請求項3又は4に記載の難透気透水性汚染土壌の浄化システム。
The system for purifying hardly permeable and air permeable contaminated soil according to claim 3 or 4, wherein the vibrator is composed of a vibrator.
JP2003307444A 2003-08-29 2003-08-29 Purification method and system for hardly air permeable and contaminated soil Expired - Fee Related JP4360157B2 (en)

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