JP2014171994A - Ground mix body, ground purification body, and purification method of contaminated soil - Google Patents

Ground mix body, ground purification body, and purification method of contaminated soil Download PDF

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JP2014171994A
JP2014171994A JP2013048034A JP2013048034A JP2014171994A JP 2014171994 A JP2014171994 A JP 2014171994A JP 2013048034 A JP2013048034 A JP 2013048034A JP 2013048034 A JP2013048034 A JP 2013048034A JP 2014171994 A JP2014171994 A JP 2014171994A
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underground
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silt
ground
contaminated
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JP6257903B2 (en
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Yoshiaki Hagino
芳章 萩野
Eiichiro Imayasu
英一郎 今安
Kazuhisa Fukunaga
和久 福永
Kazuhiro Noguchi
和宏 野口
Nobuhiko Yamashita
信彦 山下
Yasunari Yano
康成 矢納
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Osaka Gas Co Ltd
Fudo Tetra Corp
Nippon Steel Engineering Co Ltd
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Osaka Gas Co Ltd
Fudo Tetra Corp
Nippon Steel and Sumikin Engineering Co Ltd
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Abstract

PROBLEM TO BE SOLVED: To provide a ground mix body and a ground purification body suitable for purifying contaminated soil of a subsoil formed of a sand layer, and an alternation of a silt layer and a clay layer, and a purification method of contaminated soil for purifying contamination substance of a whole contaminated section surely.SOLUTION: The ground mix body is a mixed body of soil of a subsoil of the site including sand, silt, and clay and water, and is formed on a subsoil of a sand layer contaminated by a harmful substance, and on an alternation contaminated subsoil of silt and clay layers, and the ground mix body has higher water permeability than that of the silt and clay layers. The ground purification body formed by forming a well for injecting agents on the ground mix body, is also provided.

Description

本発明は、シアンや揮発性有機化合物等の有害物質で汚染された汚染土壌に構築される地中混練体、地中浄化体及びこれを利用した汚染土壌の浄化方法に関するものである。   The present invention relates to an underground kneaded body constructed in contaminated soil contaminated with harmful substances such as cyan and volatile organic compounds, an underground purifier, and a method for purifying contaminated soil using the same.

シアンや揮発性有機化合物等の有害物質による土壌汚染や地下水汚染は、砂層とシルト・粘土層の互層からなる地盤で汚染されている事例が多い。このような汚染は、第1帯水層から第2帯水層まで汚染されている例が多くある(図10参照)。特に第1帯水層と第2帯水層間のシルト・粘土層においては有害物質が吸着され高濃度汚染となっていることが多い。図10中、ハッチング部分が有害物質による汚染を示す。   In many cases, soil contamination and groundwater contamination due to toxic substances such as cyan and volatile organic compounds are contaminated in the ground consisting of sand, silt and clay layers. There are many examples of such contamination from the first aquifer to the second aquifer (see FIG. 10). In particular, in the silt / clay layer between the first aquifer and the second aquifer, harmful substances are often adsorbed and become highly contaminated. In FIG. 10, hatched portions indicate contamination by harmful substances.

従来、有害物質による汚染土壌や汚染地下水の浄化方法としては、汚染土壌に注入井戸を設けて薬剤を対象層に注入して浄化・分解・不溶化する周知の方法や、汚染土壌に微細気泡と微生物用栄養剤とを注入しながら、汚染土壌を混合攪拌する浄化方法(特開2012−40476号公報)が知られている。   Conventional methods for purifying contaminated soil and groundwater with harmful substances include well-known methods for injecting wells into contaminated soil and injecting chemicals into the target layer to purify, decompose, and insolubilize them. There is known a purification method (Japanese Patent Laid-Open No. 2012-40476) in which contaminated soil is mixed and stirred while injecting a nutrient for use.

特開2012−40476号公報JP 2012-40476 A

しかしながら、従来の周知の方法は、地下水より上の不飽和領域については適用が困難である。また、難透水層であるシルト・粘土層への均一な薬剤の浸透拡散が困難なことから汚染範囲への薬剤浸透が確実ではないという問題がある。また、特開2012−40476号公報の浄化方法は、シルト層を含まない飽和層に対する部分構築であり、シルト層に吸着した高濃度汚染の浄化を対象としたものではない。また、撹拌混合領域12以外の汚染土壌は依然として、透水性が低いものであり、栄養剤の浸透が十分ではないという問題がある。   However, conventional known methods are difficult to apply to unsaturated regions above groundwater. In addition, there is a problem that the penetration of the drug into the contaminated area is not reliable because it is difficult to uniformly diffuse the drug into the silt / clay layer, which is a hardly water permeable layer. Moreover, the purification method of JP2012-40476 is a partial construction for a saturated layer that does not include a silt layer, and is not intended for purification of high-concentration contamination adsorbed on the silt layer. Moreover, the contaminated soil other than the stirring and mixing region 12 is still low in water permeability, and there is a problem that the nutrient is not sufficiently penetrated.

従って、本発明の目的は、砂層とシルト・粘土層の互層からなる地盤の汚染土壌の浄化に好適な地中混練体及びこれを用いた地中浄化体を提供することにあり、また、更に汚染区域全体に薬剤の浸透が十分行え、シルト・粘土層に吸着した高濃度汚染物質を確実に浄化する汚染土壌の浄化方法を提供することにある。   Accordingly, an object of the present invention is to provide an underground kneaded body suitable for the purification of soil contaminated soil consisting of a sand layer and a silt / clay layer, and an underground purification body using the same. It is an object of the present invention to provide a method for remediating contaminated soil that can sufficiently infiltrate the entire contaminated area and reliably purify high-concentration contaminants adsorbed on the silt / clay layer.

かかる実情において、本発明者等は鋭意検討を行った結果、有害物質で汚染された砂層とシルト・粘土層の互層地盤に、砂、シルト及び粘土を含む現地盤土と水の混練物である透水性の高い地中混練体を形成すれば、砂層とシルト・粘土層の互層からなる地盤の汚染土壌の浄化に好適であること、更にこの地中混練体に薬剤注入用の井戸を形成した地中浄化体であれば、汚染区域全体に薬剤の浸透が十分行え、シルト・粘土層に吸着した高濃度汚染物質を確実に浄化できること等を見出し、本発明を完成するに至った。   In such a situation, the present inventors have intensively studied, and as a result, are a mixture of local soil containing sand, silt and clay and water on the alternate layer ground of sand layer and silt / clay layer contaminated with harmful substances. If an underground kneaded body with high water permeability is formed, it is suitable for purification of soil contaminated with ground consisting of sand and silt / clay layers, and further, a well for injecting chemicals is formed in the underground kneaded body. The underground purifier has been found to be able to sufficiently penetrate the entire contaminated area and reliably purify the high-concentration pollutant adsorbed on the silt / clay layer, thereby completing the present invention.

すなわち、本発明は、有害物質で汚染された砂層とシルト・粘土層の互層地盤に形成されるものであり、砂、シルト及び粘土を含む現地盤土と水の混練物であって、該シルト・粘土層の透水性より高い透水性を有することを特徴とする地中混練体を提供するものである。   That is, the present invention is formed on an alternating layer ground of a sand layer and a silt / clay layer contaminated with a harmful substance, and is a kneaded mixture of local soil containing sand, silt and clay, and water. -The underground kneaded body characterized by having a water permeability higher than the water permeability of a clay layer.

また、本発明は、前記地中混練体中に、薬剤注入用の井戸を形成したことを特徴とする地中浄化体を提供するものである。   Moreover, this invention provides the underground purification body characterized by forming the well for chemical | medical agent injection | pouring in the said underground kneading body.

また、本発明は、有害物質で汚染された砂層とシルト・粘土層の互層地盤を浄化する方法であって、撹拌装置を使用し、該汚染土壌に対して薬剤と水を注入しながら撹拌混練し、所定の深度まで貫入又は引き抜くことで、該シルト・粘土層の透水性より高い透水性を有する地中混練体を形成することを特徴とする汚染土壌の浄化方法を提供するものである。   Further, the present invention is a method for purifying an alternate layer ground of a sand layer and a silt / clay layer contaminated with harmful substances, using a stirrer and stirring and kneading while injecting chemicals and water into the contaminated soil And it provides the purification method of the contaminated soil characterized by forming the underground kneaded body which has water permeability higher than the water permeability of this silt clay layer by penetrating or pulling out to a predetermined depth.

また、本発明は、有害物質で汚染された砂層とシルト・粘土層の互層地盤を浄化する方法であって、撹拌装置を使用し、該汚染土壌に対して加水しながら撹拌混練し、所定の深度まで貫入又は引き抜くことで、該シルト・粘土層の透水性より高い透水性を有する地中混練体を形成するI工程と、該地中混練体に、薬剤注入用の井戸を形成するII工程と、該井戸に薬剤を注入して有害物質を含む地中混練体を浄化するIII工程を行うことを特徴とする汚染土壌の浄化方法を提供するものである。   Further, the present invention is a method for purifying an alternate layer ground of a sand layer and a silt / clay layer contaminated with harmful substances, using a stirring device, stirring and kneading the contaminated soil while adding water, I step for forming an underground kneaded body having water permeability higher than that of the silt / clay layer by penetrating or drawing out to a depth, and II step for forming a well for injecting a drug in the underground kneaded body And a method for purifying contaminated soil, characterized in that a step III is performed to purify the underground kneaded body containing harmful substances by injecting a chemical into the well.

本発明によれば、有害物質で汚染された砂層とシルト・粘土層の互層からなる汚染土壌の汚染区域全体に薬剤の浸透が十分行え、シルト・粘土層に吸着した高濃度汚染物質を確実に浄化できる。   According to the present invention, it is possible to sufficiently permeate the entire contaminated area of the contaminated soil consisting of sand layers and silt / clay layers contaminated with harmful substances, and to ensure that high-concentration pollutants adsorbed on the silt / clay layers are absorbed It can be purified.

本発明の実施の形態における汚染土壌の浄化方法を説明する図である。It is a figure explaining the purification method of the contaminated soil in embodiment of this invention. (A)は施工前の互層地盤の状態を、(B)は撹拌混練中の地盤の状態を、(C)は撹拌混練後の地中混練体をそれぞれ示す模式図である。(A) is a schematic diagram showing the state of the alternating layer ground before construction, (B) is the state of the ground during stirring and kneading, and (C) is a schematic view showing the ground kneaded body after stirring and kneading. 実施例における浄化の対象地盤のボーリング簡略柱状図である。It is a boring simplified columnar figure of the ground for purification in an example. 図3の符号A部の粒径加積曲線を示す。The particle size accumulation curve of the code | symbol A part of FIG. 3 is shown. 図3の符号B部の粒径加積曲線を示す。The particle size accumulation curve of the code | symbol B part of FIG. 3 is shown. 図3の符号C部の粒径加積曲線を示す。The particle size accumulation curve of the code | symbol C part of FIG. 3 is shown. 図3の符号D部の粒径加積曲線を示す。The particle size accumulation curve of the code | symbol D part of FIG. 3 is shown. 地中浄化体及び汚染土壌の浄化方法を説明する図である。It is a figure explaining the purification method of an underground purification body and contaminated soil. 本発明の浄化方法における浄化工程を説明する図である。It is a figure explaining the purification process in the purification method of the present invention. 汚染された互層地盤の模式図である。It is a schematic diagram of the contaminated alternate layer ground.

(地中混練体の説明)
次に、本発明の実施の形態における地中混練体を図1及び図2を参照して説明する。本発明の地中混練体10は、有害物質で汚染された砂層33、35とシルト・粘土層34の互層汚染地盤3に形成されるものであり、砂、シルト及び粘土を含む現地盤土と水の混練物であって、該シルト・粘土層の透水性より高い透水性を有する。
(Description of underground kneaded body)
Next, the underground kneaded body in the embodiment of the present invention will be described with reference to FIGS. The underground kneaded body 10 according to the present invention is formed on the soil layer 3 with the sand layers 33 and 35 and the silt / clay layer 34 contaminated with harmful substances. It is a water kneaded product and has a water permeability higher than that of the silt / clay layer.

互層地盤としては、砂層33とシルト・粘土層34の2層構造を含む地盤、特に、砂層33とシルト・粘土層34と砂層35の3層構造を含む地盤であり、通常、表層側の砂層33の上には、礫混じり砂を主体とする盛土層が存在していてもよい。シルト・粘土層34は、シルト層又は粘土層あるいはシルトと粘土が混在する層を言う。砂層33の透水係数は、概ね10−4〜10−2cm/秒、シルト・粘土層34の透水係数は、概ね10−7〜10−4cm/秒であり、砂層33、35は透水層とも言い、シルト・粘土層34は難透水層とも言う。砂層33は、通常帯水層である。従って、本明細書では、砂層33とシルト・粘土層34と砂層35の3層構造の地盤の場合、表層側の砂層33を第1帯水層、反表層側の砂層35を第2帯水層とも言う。 The alternate-layer ground is a ground including a two-layer structure of a sand layer 33 and a silt / clay layer 34, in particular, a ground including a three-layer structure of a sand layer 33, a silt / clay layer 34, and a sand layer 35. An embankment layer mainly composed of gravel mixed sand may be present on 33. The silt / clay layer 34 is a silt layer, a clay layer, or a layer in which silt and clay are mixed. The water permeability coefficient of the sand layer 33 is approximately 10 −4 to 10 −2 cm / second, the water permeability coefficient of the silt / clay layer 34 is approximately 10 −7 to 10 −4 cm / second, and the sand layers 33 and 35 are water permeable layers. Also, the silt / clay layer 34 is also referred to as a poorly permeable layer. The sand layer 33 is a normal aquifer. Therefore, in the present specification, in the case of a ground having a three-layer structure of the sand layer 33, the silt / clay layer 34, and the sand layer 35, the sand layer 33 on the surface layer side is the first aquifer and the sand layer 35 on the opposite surface side is the second aquifer. Also called a layer.

地中混練体が形成される地盤は、有害物質で汚染された互層地盤である。汚染領域としては、有害物質が少なくともシルト・粘土層に存在するものであればよく、有害物質が少なくとも砂層33とシルト・粘土層34と砂層35の3層まで、すなわち、第1帯水層から第2帯水層まで及んでいるものが、本発明の効果が顕著に表われる。有害物質としては、べンゼン、トルエン、エチルベンゼン、キシレン、ケトン類などを炭化水素化合物;トリクロロエチレン、テトラクロロエチレン、ジクロロエチレンなど有機塩素化合物;各種シアン化物および鉄、ニッケル、銅等各種金属のシアン錯体等のシアン化合物;ガソリン、軽油、灯油、重油、機械油、潤滑油など油脂類が挙げられる。これら例示された有害物質は、1種単独又は2種以上を含むものである。   The ground where the underground kneaded body is formed is an alternating layer ground contaminated with harmful substances. As the contaminated area, any harmful substance may be present as long as it exists in at least the silt / clay layer, and the harmful substance has at least three layers of sand layer 33, silt / clay layer 34, and sand layer 35, that is, from the first aquifer. What extends to the second aquifer exhibits the effect of the present invention remarkably. Hazardous substances include hydrocarbons such as benzene, toluene, ethylbenzene, xylene, and ketones; organochlorine compounds such as trichloroethylene, tetrachloroethylene, and dichloroethylene; cyanides such as cyanides of various cyanides and various metals such as iron, nickel, and copper Compound; Examples include oils and fats such as gasoline, light oil, kerosene, heavy oil, machine oil, and lubricating oil. These exemplified harmful substances include one kind or two or more kinds.

本発明の地中混練体は、砂、シルト及び粘土を含む現地盤土と水の混練物である。すなわち、地中混練体は、原地盤土と水の混練物であり、盛土層に含まれる礫等を含んでいてもよい。なお、地中混練体は当然に有害物質を含んでいる。また、地中混練体には、薬剤が含まれていてもよい。地中混練体に薬剤を含ませることで、その後、井戸から注入される薬剤の浄化効率を高めることができる。また、有害物質の種類や濃度によっては、その後の薬剤注入用の井戸の設置を省略することができる。薬剤としては、汚染土壌中に生息している微生物によるシアン化合物の分解を促進させるための栄養剤等が挙げられる。水は地下水及び加水された水である。加水された水には、薬剤水溶液中に含まれる水も含まれる。地中混練体は、全体が概ね均一化されるように混練されたものであるが、透水性が極めて大であるため、粗粒土が下方に、細粒土が上方に溜まり易い。   The underground kneaded body of the present invention is a kneaded product of local clay and water containing sand, silt and clay. That is, the underground kneaded body is a kneaded material of raw ground soil and water, and may contain gravel or the like contained in the embankment layer. The underground kneaded body naturally contains harmful substances. The underground kneaded body may contain a drug. By including the chemical in the underground kneaded body, the purification efficiency of the chemical injected from the well can be increased thereafter. Further, depending on the type and concentration of the harmful substance, the subsequent installation of the well for injecting the drug can be omitted. Examples of the drug include nutrients for accelerating the degradation of cyanide by microorganisms living in the contaminated soil. Water is groundwater and hydrolyzed water. Water that has been added includes water contained in the aqueous solution of the drug. The underground kneaded body is kneaded so that the whole is almost uniform. However, since the water permeability is extremely large, the coarse-grained soil tends to accumulate on the lower side and the fine-grained soil tends to accumulate on the upper side.

本発明の地中混練体は、シルト・粘土層の透水性より高い透水性を有し、好ましくはシルト・粘土層の透水係数の10倍以上、更に好ましくは100倍以上、特に好ましくは1000倍以上高い透水係数を示すものである。具体的には、地中混練体の透水係数は、10−6cm/秒以上、好ましくは10−6〜10−3cm/秒程度である。地中混練体の透水係数は、公知の原位置透水試験あるいは室内透水試験により求められる。地中混練体が上記の透水係数を示すことにより、互層地盤が、超軟弱地盤となり、薬剤の注入及び浸透が容易となり、浄化効率が向上する。 The underground kneaded body of the present invention has a water permeability higher than that of the silt / clay layer, preferably 10 times or more, more preferably 100 times or more, particularly preferably 1000 times the water permeability coefficient of the silt / clay layer. The high water permeability coefficient is shown above. Specifically, the hydraulic conductivity of the underground kneaded body is 10 −6 cm / second or more, preferably about 10 −6 to 10 −3 cm / second. The permeability coefficient of the underground kneaded body is obtained by a known in-situ permeability test or indoor permeability test. When the underground kneaded body exhibits the above-mentioned water permeability, the alternate-layered ground becomes an ultra-soft ground, which facilitates the injection and penetration of chemicals and improves the purification efficiency.

本発明の地中混練体は、ラップ施工または接円施工により広域に亘り構築することができる。すなわち、地中混練体は、汚染域全体に構築することが好ましい。これにより、汚染域内に地中混練体の未施工部分がなくなり、汚染域全体に対して薬剤が確実に浸透する。また、ラップ施工による重複施工部は、より透水性が向上する。本発明の地中混練体の形状は、例えば柱状杭、矩形状の壁体及びこれらの連続施工体、ラップ施工体または接円施工である。   The underground kneaded body of the present invention can be constructed over a wide area by lap construction or contact circle construction. That is, the underground kneaded body is preferably constructed in the entire contaminated area. As a result, there is no unconstructed portion of the underground kneaded body in the contaminated area, and the drug reliably penetrates into the entire contaminated area. Moreover, the water permeability improves more in the overlapping construction part by lap construction. The shape of the underground kneaded body of the present invention is, for example, a columnar pile, a rectangular wall body, a continuous construction body, a lap construction body, or a contact construction.

(地中浄化体)
本発明の地中浄化体は、地中混練体中に、薬剤注入用の井戸を形成したものである。薬剤注入用の井戸は、公知のものでよく、地中混練体中、適宜の個数で形成される。複数個の薬剤注入用の井戸を形成する場合、汚染域全体に薬剤が均等に行き亘るよう、概ね等間隔で設置することが好ましい。また、地下水の流れが早い地盤においては、上流側にシフトさせて設置してもよい。また、本発明の地中浄化体は、地中混練体中に、観測用井戸を形成してもよい。観測用井戸は、公知の井戸が適用でき、地下水を揚水して、該地下水中の栄養剤濃度や汚染物質濃度、水質、微生物等の地下水の状態をモニタリングするものである。
(Underground purification body)
The underground purification body of this invention forms the well for chemical | medical agent injection | pouring in the underground kneaded body. Wells for drug injection may be known ones, and are formed in an appropriate number in the underground kneaded body. In the case of forming a plurality of wells for injecting medicine, it is preferable to install them at approximately equal intervals so that the medicine is evenly distributed throughout the contaminated area. Further, in the ground where the flow of groundwater is fast, the groundwater may be shifted to the upstream side. In the underground purification body of the present invention, an observation well may be formed in the underground kneaded body. As the observation well, a known well can be applied, and the groundwater is pumped up to monitor the concentration of nutrients in the groundwater, the concentration of contaminants, the water quality, the state of the groundwater such as microorganisms, and the like.

本発明の地中浄化体は、汚染区域全域に形成することが好ましい。これにより、汚染域内に地中浄化体の未施工部分がなくなり、汚染域全体に薬剤を浸透させることができる。本発明の地中浄化体の透水係数は、本発明の地中混練体と同様の透水係数のものである。   The underground purification body of the present invention is preferably formed over the entire contaminated area. Thereby, there is no unconstructed portion of the underground purification body in the contaminated area, and the drug can penetrate into the entire contaminated area. The permeability coefficient of the underground purification body of the present invention is the same as that of the underground kneaded body of the present invention.

(汚染土壌の浄化方法)
次に、本発明の第1の実施の形態における汚染土壌の浄化方法(第1方法)について説明する。すなわち、本例の汚染土壌の浄化方法は、有害物質で汚染された砂層33とシルト・粘土34層の互層地盤3を浄化する方法である。互層地盤3であるか否かは、公知のボーリング調査及び土質調査により判断できる。図1は、汚染地盤の一例を示す。地表側から深度方向に対して、礫混じり砂である盛土層31、第1帯水層である砂層33、シルト・粘土層34、第2帯水層である砂層35からなり、符号31は不飽和層、32は飽和層である(図2(A)参照)。有害物質で汚染された汚染層Xは、これらの層の全体に亘っている。特に第1帯水層33と第2帯水層35間のシルト・粘土層34においては有害物質が吸着され高濃度汚染となっている。有害物質は、本発明の地中混練体におけるものと同様のものが挙げられる。
(Purification method of contaminated soil)
Next, the contaminated soil purification method (first method) according to the first embodiment of the present invention will be described. That is, the method for purifying contaminated soil in this example is a method for purifying the alternate layer ground 3 of the sand layer 33 and the silt / clay 34 layer contaminated with harmful substances. Whether or not it is the two-layered ground 3 can be determined by a known boring survey and soil survey. FIG. 1 shows an example of contaminated ground. From the surface side to the depth direction, it consists of the embankment layer 31 that is sand mixed with gravel, the sand layer 33 that is the first aquifer, the silt / clay layer 34, and the sand layer 35 that is the second aquifer. The saturated layer 32 is a saturated layer (see FIG. 2A). The contaminated layer X contaminated with harmful substances extends over these layers. In particular, in the silt / clay layer 34 between the first aquifer 33 and the second aquifer 35, harmful substances are adsorbed and become highly concentrated. Examples of the harmful substance are the same as those in the underground kneaded body of the present invention.

本例の汚染土壌の浄化方法において、I工程は、撹拌装置1を使用し、汚染土壌Xに対して加水しながら撹拌混練し、所定の深度まで貫入又は引き抜くことで、該シルト・粘土層の透水性より高い透水性を有する地中混練体を形成する工程である。撹拌装置1としては、深層混合処理工法や地中柱状杭造成工法で使用される公知の撹拌翼11を備える撹拌装置1あるいは公知のトレンチャーを使用することができる。撹拌翼11を備える撹拌装置1における撹拌翼11としては、両翼(2枚)の2段羽根又は3段羽根の水平撹拌翼が好適である。このような撹拌装置1を使用することで、汚染土壌X(互層地盤)を所定の深度及び所定の径で撹拌混合することができる。なお、符号2は、水供給装置又は薬剤水溶液供給装置である。以下、撹拌翼11を備える撹拌装置1を使用する場合の浄化方法について説明する。   In the method for purifying contaminated soil of this example, the step I uses the stirring device 1 to stir and knead the contaminated soil X while adding water, and penetrates or pulls out to a predetermined depth. It is a step of forming an underground kneaded body having higher water permeability than water permeability. As the stirring device 1, the stirring device 1 provided with the well-known stirring blade 11 used by a deep-layer mixing process method or an underground columnar pile construction method, or a well-known trencher can be used. As the stirring blade 11 in the stirring device 1 including the stirring blade 11, a two-stage blade of two blades (two) or a horizontal stirring blade of a three-stage blade is preferable. By using such a stirring device 1, the contaminated soil X (alternate ground) can be stirred and mixed at a predetermined depth and a predetermined diameter. Reference numeral 2 denotes a water supply device or a chemical aqueous solution supply device. Hereinafter, the purification method in the case of using the stirring apparatus 1 provided with the stirring blade 11 is demonstrated.

I工程において、撹拌装置1の回転軸12の軸芯を汚染土壌Xの撹拌混練地点の中心に一致させる。次いで、撹拌装置1を駆動し撹拌翼11を回転させながら回転軸12を地中に貫入させる。この際、加水しながら撹拌混練する。加水しながら撹拌混練することで、透水性の高い超軟弱地盤を形成することができる。なお、加水量は、土壌に含まれる含水率、撹拌領域及び得られる混練物の透水係数等を考慮して決定されるが、撹拌混練地盤に対して、概ね5〜20体積%である。   In step I, the axis of the rotating shaft 12 of the stirring device 1 is made to coincide with the center of the stirring and kneading point of the contaminated soil X. Next, the rotating shaft 12 is penetrated into the ground while the stirring device 1 is driven to rotate the stirring blade 11. At this time, the mixture is stirred and kneaded while adding water. By stirring and kneading while adding water, an ultra-soft ground with high water permeability can be formed. In addition, although the amount of water is determined in consideration of the moisture content contained in the soil, the stirring region, the hydraulic conductivity of the obtained kneaded material, and the like, it is approximately 5 to 20% by volume with respect to the stirring kneaded ground.

撹拌混練は、貫入時又は引き抜き時あるいは貫入時と引き抜き時の両時であり、好ましくは貫入時と引き抜き時の両時である。貫入速度及び引き抜き速度は、均一性の高い混練物を得るための好適な速度として決定すればよい。このような操作により、礫、細粒土及び粗粒土が十分に撹拌され、均一性及び透水性の高い混練物が得られる。図2(B)に示すように、撹拌混練区域は、砂層、シルト・粘土層の区別がなくなり、透水性の高い超軟弱の土壌となるため、均一撹拌をしつつも、粗粒土が下方に、細粒土が上方に溜まる傾向となる。I工程においては、撹拌混練しつつ、薬剤を同時に投入してもよい。有害物質が薬剤による前処理が必要となる場合、I工程において、前処理用薬剤を注入して前処理を行えば、その後のIII工程における浄化処理が効率的に行える。なお、I工程において薬剤を投入する際、薬剤が水を含む場合、単独の水の注入を省略できる。   The stirring and kneading is at the time of penetration or at the time of withdrawal or at the time of penetration and at the time of withdrawal, preferably both at the time of penetration and at the time of withdrawal. The penetration speed and the drawing speed may be determined as suitable speeds for obtaining a highly uniform kneaded product. By such an operation, gravel, fine-grained soil and coarse-grained soil are sufficiently stirred, and a kneaded product having high uniformity and water permeability is obtained. As shown in FIG. 2 (B), the agitation and kneading zone has no distinction between the sand layer and the silt / clay layer, and becomes ultra-soft soil with high water permeability. In addition, fine-grained soil tends to accumulate upward. In step I, the chemicals may be added simultaneously while stirring and kneading. When the pretreatment with a chemical | medical agent is required for a hazardous | toxic substance, if the pretreatment chemical | medical agent is inject | poured and performed in the I process, the purification process in subsequent III processes can be performed efficiently. In addition, when inject | pouring a chemical | medical agent in I process, when a chemical | medical agent contains water, injection | pouring of single water can be skipped.

I工程においては、撹拌混練により、シルト・粘土層34の透水性より高い透水性を有する地中混練体10aを得る(図2(C))。すなわち、撹拌混練により、シルト・粘土層の透水係数の10倍以上、更に好ましくは100倍以上、特に好ましくは1000倍以上高い透水係数を示す地中混練体10aを得る。具体的には、地中混練体の透水係数は、10−6cm/秒以上、好ましくは10−6〜10−3cm/秒程度である。なお、透水係数は、互層地盤において砂と粘土の体積割合で決まる。また、加水量は、原地盤の含水量に応じて調整される。 In the step I, the ground kneaded body 10a having water permeability higher than that of the silt / clay layer 34 is obtained by stirring and kneading (FIG. 2C). That is, by stirring and kneading, an underground kneaded body 10a exhibiting a water permeability of 10 times or more, more preferably 100 times or more, particularly preferably 1000 times or more that of the silt / clay layer is obtained. Specifically, the hydraulic conductivity of the underground kneaded body is 10 −6 cm / second or more, preferably about 10 −6 to 10 −3 cm / second. The hydraulic conductivity is determined by the volume ratio of sand and clay in the alternating layer ground. The amount of water added is adjusted according to the water content of the original ground.

柱状の地中混練体10aは、汚染地盤X中に多数形成され、好ましくは、汚染区域全域に形成される。これにより、汚染領域全域を透水性の高い超軟弱地盤とすることができ、汚染の浄化を確実に行える。柱状の地中混練体10aを汚染地盤X中に多数形成する場合、ラップ施工で形成することが好ましい。これにより、汚染地盤全域を効率的に超軟弱地盤とすることができる。また、ラップ施工または接円施工による重複施工部は、より透水性が向上する。   A large number of columnar underground kneaded bodies 10a are formed in the contaminated ground X, and preferably formed in the entire contaminated area. As a result, the entire contaminated area can be made into an ultra-soft ground with high water permeability, and contamination can be reliably purified. When a large number of columnar underground kneaded bodies 10a are formed in the contaminated ground X, it is preferable to form them by lapping. As a result, the entire contaminated ground can be efficiently made into an ultra-soft ground. Moreover, the water permeability improves more in the overlapping construction part by lap construction or contact circle construction.

II工程は、地中混練体に、薬剤注入用の井戸を形成する工程である。すなわち、図9に示すように、汚染区域に構築された地中混練体10bに、薬剤注入用の井戸13を形成する。薬剤注入用の井戸は、先端がスクリーン管である管状体を建て込んだ公知の井戸が使用でき、例えば、特開2009−6304号公報に記載のものが挙げられる。薬剤注入用の井戸は、地中混練体中、適宜の個数で形成される。複数個の薬剤注入用の井戸を形成する場合、汚染域全体に薬剤が均等に行き亘るよう、等間隔で設置することが好ましい。   Step II is a step of forming a well for drug injection in the underground kneaded body. That is, as shown in FIG. 9, a well 13 for injecting a drug is formed in the underground kneaded body 10b constructed in the contaminated area. As the well for drug injection, a known well in which a tubular body whose tip is a screen tube is built can be used, and examples include those described in JP-A-2009-6304. Wells for injecting chemicals are formed in an appropriate number in the underground kneaded body. When forming a plurality of wells for injecting drugs, it is preferable to install them at equal intervals so that the drugs are evenly distributed throughout the contaminated area.

III工程は、井戸13に薬剤を注入して汚染土壌を浄化する工程である。薬剤は、地中浄化体における薬剤と同様であり、汚染土壌中に生息している微生物によるシアン化合物の分解を促進させるための栄養剤等が挙げられる。井戸13に薬剤を注入して汚染土壌を浄化する方法としては、自然流下法及び圧力注入であるダブルパッカー法等の公知の方法が適用できる。井戸13に注入された薬剤は、図9に示すように、ラップ施工された地中混練体10bの透水性が高いため、汚染地盤X全域に浸透する。そして、汚染地盤X全域に薬剤が浸透することにより、汚染土壌中に生息している微生物が活性化し、微生物によるシアン化合物の分解が促進される。   Step III is a step of purifying contaminated soil by injecting chemicals into the well 13. The drug is the same as the drug in the underground purification body, and examples thereof include a nutrient for promoting the decomposition of cyanide compounds by microorganisms living in the contaminated soil. As a method for injecting a chemical into the well 13 to purify the contaminated soil, known methods such as a natural flow method and a double packer method which is pressure injection can be applied. As shown in FIG. 9, the drug injected into the well 13 penetrates the entire contaminated ground X because the underground kneaded body 10 b subjected to lapping has high water permeability. And since the chemical | medical agent osmose | permeates the contaminated ground X whole area, the microorganisms which inhabit in the contaminated soil will be activated, and decomposition | disassembly of the cyanide by microorganisms will be accelerated | stimulated.

次に、本発明の第2の実施の形態における汚染土壌の浄化方法(第2方法)について説明する。すなわち、本例の汚染土壌の浄化方法は、有害物質で汚染された砂層とシルト・粘土層の互層地盤を浄化する方法であって、撹拌翼を備える撹拌装置を使用し、該汚染土壌に対して薬剤と水を注入しながら撹拌混練し、所定の深度まで貫入又は引き抜くことで、該シルト・粘土層の透水性より高い透水性を有する地中混練体を形成する方法である。第2方法において、第1方法と異なる点は、薬剤の注入をI工程で行ない、薬剤注入用の井戸を設置せず、汚染地盤を浄化するものである。   Next, a method for purifying contaminated soil (second method) according to the second embodiment of the present invention will be described. That is, the method for purifying contaminated soil in this example is a method for purifying an alternate layer ground of a sand layer and a silt / clay layer contaminated with harmful substances, using a stirring device equipped with stirring blades, This is a method of forming an underground kneaded body having a water permeability higher than that of the silt / clay layer by stirring and kneading while injecting a drug and water, and penetrating or withdrawing to a predetermined depth. The second method is different from the first method in that the injection of the drug is performed in the I step, the well for the drug injection is not installed, and the contaminated ground is purified.

第2方法においては、第1方法と異なる点についてのみ説明する。すなわち、薬剤は撹拌混練中に撹拌区域に注入される。薬剤の注入は、撹拌混練中であれば、水の注入と同じであっても、異なっていてもよい。薬剤と水は、薬剤と単独の水であっても、あるいは水を含む薬剤であってもよい。従って、水を含む薬剤の場合、単独の水の注入を省略できる場合がある。汚染土壌に対して薬剤を注入しながら撹拌混練することで、地中混練体には、薬剤が均一に含まれることになる。また、地中混練体をラップ施工したラップ施工体にも、同様に、薬剤が均一に含まれることになる。この第2方法により得られた地中混練体の透水係数は、第1方法により得られる地中混練体の透水係数と同様である。第2方法により得られた地中混練体は、互層地盤中の特にシルト・粘土層に吸着した有害物質を含んでおり、薬剤の注入効果により、有害物質を浄化できる。   In the second method, only differences from the first method will be described. That is, the drug is injected into the stirring zone during stirring and kneading. The injection of the drug may be the same as or different from the injection of water as long as it is during stirring and kneading. The drug and water may be a drug and water alone or a drug containing water. Therefore, in the case of a medicine containing water, it may be possible to omit injection of single water. By stirring and kneading while pouring the chemical into the contaminated soil, the underground kneaded body contains the chemical uniformly. Similarly, the wrap construction body in which the underground kneaded body is lapped also contains the drug uniformly. The hydraulic conductivity of the underground kneaded body obtained by this second method is the same as the hydraulic conductivity of the underground kneaded body obtained by the first method. The underground kneaded body obtained by the second method contains harmful substances adsorbed particularly on the silt / clay layer in the alternate layered ground, and the harmful substances can be purified by the injection effect of the drug.

本発明の汚染土壌の浄化方法においては、更に、地中混練体中に、観測用井戸を形成する工程を実施してもよい。観測用井戸は、前記の観測用井戸と同様である。   In the contaminated soil purification method of the present invention, a step of forming an observation well in the underground kneaded body may be further performed. The observation well is the same as the observation well described above.

(実施例)
次に、実施例を挙げて本発明を更に具体的に説明するが、これは単に例示であって、本発明を制限するものではない。
(Example)
EXAMPLES Next, although an Example is given and this invention is demonstrated more concretely, this is only an illustration and does not restrict | limit this invention.

(地中混練体の形成)
ボーリング調査及び土質調査により、互層地盤(試験地盤)を選定した。その互層地盤のボーリング簡略柱状図を図3に示す。図3の地盤は、表面より深さ方向に対して、盛土(礫混じり砂)層、盛土(礫混じり砂炭ガラ混じり砂)層、盛土(シルト質砂)層、埋土(細砂)層、埋土(粘土)層、埋土(砂)層を有するものであった。この中、盛土(シルト質砂)層(符号;A)の粒径加積曲線を図4に示し、埋土(細砂)層(符号;B)の粒径加積曲線を図5に示し、埋土(粘土)層上部(符号;C)の粒径加積曲線を図6に示し、埋土(粘土砂)層下部(符号;D)の粒径加積曲線を図7に示した。また、この地盤の地下水位は−1.2mの位置であり、埋土(粘土)層の透水係数(室内混練試験)は、2.25×10−7cm/秒であった。また、互層地盤中の初期TOC(全有機炭素)溶出濃度は、8.2mg/Lであった。なお、この互層地盤は試験用であり、薬剤の浸透拡散状態をみるものである。
(Formation of underground kneaded body)
The alternate ground (test ground) was selected by the boring survey and soil survey. FIG. 3 shows a simplified boring column diagram of the alternate layer ground. The ground shown in Fig. 3 has an embankment (sand mixed with gravel) layer, an embankment (sand mixed with sand and charcoal sand) layer, an embankment (silty sand) layer, and a buried (fine sand) layer in the depth direction from the surface. And a buried (clay) layer and a buried (sand) layer. Among these, the particle size accumulation curve of the embankment (silty sand) layer (symbol; A) is shown in FIG. 4, and the particle size accumulation curve of the buried soil (fine sand) layer (symbol; B) is shown in FIG. FIG. 6 shows the particle size accumulation curve of the upper part of the buried soil (clay) layer (symbol; C), and FIG. 7 shows the particle size accumulation curve of the lower part of the buried soil (clay sand) layer (symbol; D). . The groundwater level of this ground was -1.2 m, and the hydraulic conductivity (indoor kneading test) of the buried (clay) layer was 2.25 × 10 −7 cm / sec. In addition, the initial TOC (total organic carbon) elution concentration in the alternating layer ground was 8.2 mg / L. In addition, this alternate layer ground is for a test, and sees the osmosis | permeation diffusion state of a chemical | medical agent.

次いで、両翼3段の撹拌翼を備える撹拌装置を使用し、上記互層地盤に対して、20体積%の加水をしながら貫入時と引き抜き時に撹拌混練することで、高い透水性を有する直径1.3mの地中混練体を形成した。なお、撹拌装置は、表層より撹拌しつつ貫入し、高い透水性を得るための実質的な撹拌混練区域は、深度2mから7mまでの5mとした。なお、撹拌混練時間は20分であった。なお、回転軸の回転速度は、貫入時19rpm、引き抜き時は38rpm、貫入速度は0.4m/分〜0.7m/分、引き抜き速度は0.6〜1.1m/分であった。   Next, using a stirrer equipped with a three-stage stirrer blade on both blades, the above-mentioned alternate layer ground is stirred and kneaded at the time of penetration and withdrawing while adding 20% by volume of water. A 3 m underground kneaded body was formed. The stirring device penetrated from the surface layer while stirring, and the substantial stirring and kneading area for obtaining high water permeability was 5 m from a depth of 2 m to 7 m. The stirring and kneading time was 20 minutes. The rotational speed of the rotating shaft was 19 rpm when penetrating, 38 rpm when pulling, the penetrating speed was 0.4 m / min to 0.7 m / min, and the pulling speed was 0.6 to 1.1 m / min.

次いで、地中混練体の深さ方向のA、B、C及びD地点における土壌を採取し、粒度分析を行った。地中混練体における盛土(シルト質砂)層(符号;A)該当部分の粒径加積曲線を図4に示し、地中混練体における埋土(細砂)層(符号;B)該当部分の粒径加積曲線を図5に示し、地中混練体における埋土(粘土)層上部(符号;C)該当部分の粒径加積曲線を図6に示し、地中混練体における埋土(砂)層下部(符号;D)該当部分の粒径加積曲線を図7に示した。なお、符号A〜Dで示される各層の撹拌混練前後の粒度分析は、同じ互層地盤区域中の他の異なる3箇所でも行ったが、それぞれ同様の粒径加積曲線を示した。   Next, soil at points A, B, C, and D in the depth direction of the underground kneaded body was collected and subjected to particle size analysis. The particle size accumulation curve of the corresponding portion of the embankment (silty sand) layer (symbol; A) in the underground kneaded body is shown in FIG. 4, and the corresponding portion of the buried (fine sand) layer (symbol; B) in the underground kneaded body 5 shows the particle size accumulation curve, and FIG. 6 shows the particle size accumulation curve of the upper part (sign: C) of the buried (clay) layer in the underground kneaded body. The particle size accumulation curve at the lower part of the (sand) layer (symbol: D) is shown in FIG. In addition, although the particle size analysis before and behind stirring kneading | mixing of each layer shown by code | symbol AD was performed also in three different different places in the same alternating layer ground area, each showed the same particle size accumulation curve.

図5のB点の結果から、細砂層は、均質な細砂であったものが、撹拌混練により、不均質で粗粒を含むものとなったことが判る。また、図6及び図7のC点及びD点の結果から、粘土層は、均質な高塑性粘土のものが、撹拌混練により、粗粒を含むものとなったことが判る。また、撹拌混練物の上方部は下方部より不均質で粗粒を多く含むものであったが、概ね均質なものであった。なお、地中混練体の透水係数は、3.34×10−6cm/秒(室内混練試験)、3.85×10−6cm/秒(原位置混練試験)であり、元の粘土層の約10倍高い透水係数であった。このように、加水混練により、互層地盤は、劇的な組成変化をもたらすものであった。 From the result of point B in FIG. 5, it can be seen that the fine sand layer was homogeneous fine sand but became non-homogeneous and coarse particles by stirring and kneading. Moreover, it can be seen from the results of points C and D in FIGS. 6 and 7 that the clay layer was made of a homogeneous high-plastic clay and contained coarse particles by stirring and kneading. Moreover, although the upper part of the stirring kneaded material was heterogeneous and contained more coarse particles than the lower part, it was generally homogeneous. In addition, the hydraulic conductivity of the underground kneaded body is 3.34 × 10 −6 cm / sec (indoor kneading test), 3.85 × 10 −6 cm / sec (in-situ kneading test), and the original clay layer The water permeability was about 10 times higher. Thus, the alternate layer ground caused dramatic composition change by the hydro-kneading.

(ラップ施工された地中混練体)
図8に示すように、7本の直径1.3m、深度2〜7mまでの5mの高さの地中混練体を、直径約3.5mの仮想汚染地盤域Yにラップ施工した。ラップ施工された地中混練体は、中央の1本の柱状地中混練体に対して、円周方向に並ぶ6本の柱状地中混練体をラップ施工したものである。
(Underground kneaded body with lapping)
As shown in FIG. 8, seven underground kneaded bodies having a height of 5 m having a diameter of 1.3 m and a depth of 2 to 7 m were lapped on a virtual contaminated ground area Y having a diameter of about 3.5 m. The underground kneaded body subjected to wrapping is obtained by lapping six columnar underground kneaded bodies arranged in the circumferential direction with respect to one central columnar underground kneaded body.

(地中浄化体及び薬剤の浸透拡散試験)
図8に示すラップ施工された地中混練体の中心に、注入井戸81を形成した。また、グルコース及び各種アミノ酸を含有する市販の薬剤を注入井戸81に対してダブルパッカー法により注入した。なお、薬剤注入直後に、注入井戸81から放射状に延びる3方向(A方向、B方向、C方向)の所定位置にそれぞれボーリングを実施し、土壌を採取して土壌中のTOC濃度(mg/kg)を測定した。測定結果を表1〜表3に示した。なお、ボーリング位置は、A方向において、注入井戸81から0.5m、1.0m及び1.5mの位置(それぞれA1、A2、A3)、B方向において、注入井戸81から0.5m、1.0m及び1.5mの位置(それぞれB1、B2、B3)、C方向において、注入井戸81から0.5m、1.0m及び1.5mの位置(それぞれC1、C2、C3)である。また、表中、深度上部は、深度2.27m〜3.68mを、深度下部は、深度4.42m〜5.23mを言い、それぞれ深さ方向に異なる3地点の平均値で示した。なお、薬剤注入直後にボーリングを実施し土壌採取した理由は、薬剤由来のTOCは混練地盤中に浸透拡散するものの、時間経過と共に、微生物分解により数値が低下していくため、微生物分解の影響を極力回避するためである。また、測定されたTOC濃度の比較対象となる基準のTOC濃度は、薬剤を投入していない加水条件が同じ地中混練体でのTOC濃度とした。この基準となるTOC濃度は、別途、互層地盤の地中混練体を実験室的に再現し、同じ加水条件で得られた地盤のTOC濃度(31.01mg/kg)である。深度上部、深度下部ともに地中混練体は、理想的に均一とみなし、バックグラウンド値としてのTOC濃度31.01mg/kgに対して、薬剤由来のTOC濃度の増加傾向を見ることになる。なお、表1〜表3中、基準TOC濃度は、「基準値」として示した。
(Infiltration and diffusion test of underground purifiers and drugs)
An injection well 81 was formed in the center of the underground kneaded body shown in FIG. Moreover, the commercially available chemical | medical agent containing glucose and various amino acids was inject | poured with respect to the injection well 81 by the double packer method. Immediately after drug injection, boring is performed at predetermined positions in three directions (A direction, B direction, and C direction) extending radially from the injection well 81, and the soil is collected and the TOC concentration in the soil (mg / kg) ) Was measured. The measurement results are shown in Tables 1 to 3. The boring positions are 0.5 m, 1.0 m, and 1.5 m from the injection well 81 in the A direction (A1, A2, and A3, respectively), and 0.5 m from the injection well 81 in the B direction. The positions are 0 m and 1.5 m (B1, B2, and B3, respectively), and 0.5 m, 1.0 m, and 1.5 m from the injection well 81 (C1, C2, and C3, respectively) in the C direction. Further, in the table, the upper part of the depth means the depth of 2.27 m to 3.68 m, and the lower part of the depth means the depth of 4.42 m to 5.23 m, which are shown as average values at three different points in the depth direction. The reason for collecting the soil by drilling immediately after the injection of the drug is that although the TOC derived from the drug penetrates and diffuses into the kneaded ground, the value decreases due to microbial decomposition over time. This is to avoid as much as possible. In addition, the reference TOC concentration to be compared with the measured TOC concentration was the TOC concentration in the underground kneaded body under the same water addition conditions where no chemical was added. The reference TOC concentration is a ground TOC concentration (31.01 mg / kg) separately obtained by experimentally reproducing an underground kneaded body of an alternating layer ground and under the same water conditions. The underground kneaded body is considered to be ideally uniform in both the upper and lower depths, and an increasing tendency of the drug-derived TOC concentration is seen with respect to the TOC concentration of 31.01 mg / kg as the background value. In Tables 1 to 3, the reference TOC concentration is shown as “reference value”.

Figure 2014171994
Figure 2014171994

Figure 2014171994
Figure 2014171994

Figure 2014171994
Figure 2014171994

表1〜表3の結果から、A方向、B方向、C方向の一部を除いたほとんどの地点及び深度においても、バラツキはあるものの、基準TOC濃度より遥かに高いものであり、薬剤由来のTOCが存在することが確認された。なお、表1〜表3に示す薬剤由来のTOC濃度であれば、炭化水素化合物等の有害物質を浄化できることは実験室等により確認されている。また、各点における有害物質を完全に浄化できる目標濃度に対して小さい場合は、薬剤使用量等の増加を、大きい場合は、薬剤使用量等の減少により対応すればよい。   From the results of Tables 1 to 3, although there are variations at almost all points and depths excluding a part of the A direction, B direction, and C direction, they are much higher than the reference TOC concentration and are derived from drugs. The presence of TOC was confirmed. In addition, it has been confirmed by laboratories or the like that harmful substances such as hydrocarbon compounds can be purified with the TOC concentrations derived from the drugs shown in Tables 1 to 3. In addition, when the target concentration that can completely purify harmful substances at each point is small, an increase in the amount of drug used may be increased, and when large, a decrease in the amount of drug used may be handled.

本発明によれば、有害物質で汚染された砂層とシルト・粘土層の互層からなる汚染土壌の汚染区域全体に薬剤の浸透が十分行え、シルト・粘土層に吸着した高濃度汚染物質を確実に浄化できる。このため、VOCsやシアン等の有害物質による汚染された地盤の跡地利用が進む。   According to the present invention, it is possible to sufficiently permeate the entire contaminated area of the contaminated soil consisting of sand layers and silt / clay layers contaminated with harmful substances, and to ensure that high-concentration pollutants adsorbed on the silt / clay layers are absorbed It can be purified. For this reason, the use of the ruins of the ground contaminated with harmful substances such as VOCs and cyan is advanced.

1 撹拌装置
2 水供給装置
3 互層地盤
10 地中混練体
33、35 砂層
34 シルト・粘土層
81 注入井戸
82 ボーリング位置
DESCRIPTION OF SYMBOLS 1 Stirring device 2 Water supply device 3 Alternating ground 10 Underground kneaded body 33, 35 Sand layer 34 Silt and clay layer 81 Injection well 82 Boring position

Claims (11)

有害物質で汚染された砂層とシルト・粘土層の互層地盤に形成されるものであり、砂、シルト及び粘土を含む現地盤土と水の混練物であって、該シルト・粘土層の透水性より高い透水性を有することを特徴とする地中混練体。   It is formed in the alternate ground of sand layer and silt / clay layer contaminated with harmful substances, and is a kneaded mixture of local soil and water containing sand, silt and clay, and water permeability of the silt / clay layer An underground kneaded body characterized by having higher water permeability. 該シルト・粘土層の透水係数より10倍以上高い透水係数であることを特徴とする請求項1記載の地中混練体。   The underground kneaded body according to claim 1, wherein the underground kneaded body has a water permeability of 10 times or more higher than that of the silt / clay layer. ラップ施工または接円加工により形成されたものであることを特徴とする請求項1又は2記載の地中混練体。   3. The underground kneaded body according to claim 1 or 2, wherein the underground kneaded body is formed by lapping or circle contact processing. 薬剤を含有することを特徴とする請求項1〜3のいずれか1項に記載の地中混練体。   The underground kneaded body according to any one of claims 1 to 3, further comprising a drug. 請求項1〜4のいずれか1項に記載の地中混練体中に、薬剤注入用の井戸を形成したことを特徴とする地中浄化体。   The underground purification body which formed the well for chemical | medical agent injection | pouring in the underground kneading body of any one of Claims 1-4. 汚染区域の全域に形成したことを特徴とする請求項5記載の地中浄化体。   6. The underground purification body according to claim 5, wherein the underground purification body is formed over the entire contaminated area. 有害物質で汚染された砂層とシルト・粘土層の互層地盤を浄化する方法であって、撹拌装置を使用し、該汚染土壌に対して薬剤と水を注入しながら撹拌混練し、所定の深度まで貫入又は引き抜くことで、該シルト・粘土層の透水性より高い透水性を有する地中混練体を形成することを特徴とする汚染土壌の浄化方法。   A method for purifying an alternating layer of a sand layer and a silt / clay layer contaminated with harmful substances, using a stirrer, stirring and kneading the chemical and water into the contaminated soil, to a predetermined depth A method for purifying contaminated soil, characterized by forming an underground kneaded body having a permeability higher than that of the silt / clay layer by penetration or extraction. 前記薬剤と水は、薬剤と単独の水であるか、または水を含む薬剤であることを特徴とする請求項7記載の汚染土壌の浄化方法。   The said chemical | medical agent and water are chemical | medical agents and independent water, or are chemical | medical agents containing water, The purification method of the contaminated soil of Claim 7 characterized by the above-mentioned. 有害物質で汚染された砂層とシルト・粘土層の互層地盤を浄化する方法であって、撹拌装置を使用し、該汚染土壌に対して加水しながら撹拌混練し、所定の深度まで貫入又は引き抜くことで、該シルト・粘土層の透水性より高い透水性を有する地中混練体を形成するI工程と、
該地中混練体に、薬剤注入用の井戸を形成するII工程と、
該井戸に薬剤を注入して有害物質を含む地中混練体を浄化するIII工程を行うことを特徴とする汚染土壌の浄化方法。
It is a method for purifying the alternate layer ground of sand layer and silt / clay layer contaminated with harmful substances, using a stirrer, stirring and kneading while adding water to the contaminated soil, and penetrating or extracting to a predetermined depth. And the I step of forming an underground kneaded body having a water permeability higher than that of the silt / clay layer,
II step of forming a well for drug injection in the underground kneaded body,
A method for purifying contaminated soil, comprising performing a step III of purifying an underground kneaded body containing harmful substances by injecting a chemical into the well.
該I工程の撹拌混練において、薬剤を注入することを特徴とする請求項9記載の汚染土壌の浄化方法。   The method for purifying contaminated soil according to claim 9, wherein a chemical is injected in the stirring and kneading in the step I. 該地中混練体の透水係数は、該シルト・粘土層の透水係数より10倍以上高いことを特徴とする請求項7〜10のいずれか1項に記載の汚染土壌の浄化方法。   The method for purifying contaminated soil according to any one of claims 7 to 10, wherein a permeability coefficient of the underground kneaded body is 10 times or more higher than a permeability coefficient of the silt / clay layer.
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