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JP7616639B2 - Soil reformation state measuring method and soil reformation state measuring device - Google Patents
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JP7616639B2 - Soil reformation state measuring method and soil reformation state measuring device - Google Patents

Soil reformation state measuring method and soil reformation state measuring device Download PDF

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JP7616639B2
JP7616639B2 JP2020204953A JP2020204953A JP7616639B2 JP 7616639 B2 JP7616639 B2 JP 7616639B2 JP 2020204953 A JP2020204953 A JP 2020204953A JP 2020204953 A JP2020204953 A JP 2020204953A JP 7616639 B2 JP7616639 B2 JP 7616639B2
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正行 大石
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Daiki Rika Kogyo Co Ltd
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  • Investigation Of Foundation Soil And Reinforcement Of Foundation Soil By Compacting Or Drainage (AREA)
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Description

本発明は、土壌に改質材を導入して地盤改質する際に、その改質状況を測定するための方法等に関する。 The present invention relates to a method for measuring the state of soil modification when modifying the soil by introducing a modifier.

従来、耐震性の向上や、重金属の溶出抑制等を目的として地盤を改良する為に、地盤中に改質材を導入する手法が採用されている。この改質材には、セメントミルク(セメント系固化剤)、石灰系固化材、セメントと石灰を混合した複合系固化材、高分子系固化材、無機・有機の硬化剤と水ガラス等を用いるグラウト材等が存在する。 Traditionally, methods of introducing modifiers into the ground have been used to improve the ground's earthquake resistance and to prevent the elution of heavy metals. These modifiers include cement milk (cement-based solidifier), lime-based solidifier, composite solidifiers that are a mixture of cement and lime, polymer-based solidifiers, and grout materials that use inorganic and organic hardeners and water glass, etc.

地盤改良工法には様々存在し、例えば、地表面から深さ2m程度までの地盤改良を行う際は、バックホーやスタビライザーを用いて、粉黛状のセメント系あるいは石灰系の固化材(改質材)を散布して、軟弱土と撹拌して混合する。 There are various ground improvement methods. For example, when improving the ground from the surface to a depth of about 2m, a backhoe or stabilizer is used to spread powdered cement- or lime-based solidification material (modifier) and mix it with the soft soil.

また、地表面から深さ1m~15m程度の中層の地盤改良を行う際は、例えば、トレンチャー式工法が採用される。トレンチャー式工法では、バケット状の撹拌体をチェーン等で繋いで鉛直方向に循環回転させる掘削機や、撹拌翼の回転させる掘削機等を利用して、地中の土と改質材と撹拌混合する。 When carrying out ground improvement work in the middle layers, about 1 to 15 meters deep from the ground surface, for example, a trencher method is used. In the trencher method, an excavator that rotates a bucket-shaped agitator vertically by connecting it with a chain or the like, or an excavator that rotates an agitator blade, is used to mix and stir the soil underground with the modifier.

更に、地表面から深さ10m以上の深層の地盤改良を行う際は、例えば、撹拌翼の回転させる掘削機等を利用して地中の土と改質材と撹拌混合する手法の他に、高圧噴射撹拌工法が採用される場合が多い。高圧噴射撹拌工法にも様々あり、改質材と同時又は別々に、エアや水を高圧ジェット噴射して、改質材と土を撹拌混合したり、地中に対して高圧ジェットによって改質材を直接噴射して、土壌と改質材を撹拌混合したりする。いずれにしろ、この高圧噴射撹拌工法では、気体や液体のジェット噴射の勢いによって混合する構造であることから、改質材によって地盤が改良された範囲を早期に測定することが不可欠となる。 Furthermore, when carrying out ground improvement work at depths of 10m or more from the ground surface, in addition to the method of mixing and stirring the soil and modifier underground using an excavator with rotating mixing blades, high-pressure jet mixing methods are often used. There are various high-pressure jet mixing methods, such as high-pressure jet injection of air or water simultaneously with or separately from the modifier to mix and stir the modifier and soil, or high-pressure jet injection of the modifier directly into the ground to mix the soil and modifier. In either case, this high-pressure jet mixing method uses the force of the jet injection of gas or liquid to mix the materials, making it essential to measure the extent to which the ground has been improved by the modifier as early as possible.

例えば、特許文献1では、高圧ジェットを噴射する掘削孔から、土中の水平方向(径方向)に棒状部材を貫入して、pH又は温度を測定することで、地盤の改良範囲を測定する技術が提案されている。 For example, Patent Document 1 proposes a technology to measure the extent of ground improvement by penetrating a rod-shaped member horizontally (radially) into the soil from a borehole through which a high-pressure jet is injected and measuring the pH or temperature.

また例えば、特許文献2では、高圧ジェットを噴射する掘削孔から離れた地点において、カメラ付きロッドを地盤中に貫入し、カメラによって撮像された画像をモニターに表示して、改質材液の存在を確認することで、地盤の改良範囲を測定する技術が提案されている。 For example, Patent Document 2 proposes a technology to measure the extent of ground improvement by penetrating a rod equipped with a camera into the ground at a point away from the borehole from which the high-pressure jet is injected, displaying the image captured by the camera on a monitor, and confirming the presence of the modifying agent liquid.

特許第4721268号Patent No. 4721268 特許第4886921号Patent No. 4886921

しかしながら、特許文献1では、土中において水平方向に棒状部材を貫入すると、その貫入孔を利用して改質材が拡散する可能性があり、地盤の改良範囲を正しく測定することが難しい。これを解消するためには、改質材が硬化するまで待機してから貫入孔を形成する必要があり、測定効率が低下すると共に、硬化後では、改質不要を発見した後の補修が難しいという問題がある。 However, in Patent Document 1, when a rod-shaped member is inserted horizontally into the soil, there is a possibility that the modifier will diffuse through the penetration hole, making it difficult to accurately measure the area of ground improvement. To solve this problem, it is necessary to wait until the modifier hardens before forming the penetration hole, which reduces measurement efficiency and poses the problem that after hardening, it is difficult to carry out repairs after discovering that no modification is necessary.

また、特許文献2では、貫入孔の内周壁の画像によって、改質材液の存在を判別することが難しいという問題がある。それ故に、特許文献2では、改質材を着色する着色剤を散布してから、カメラで内壁を測定する必要があるが、土中で着色剤と改質剤を反応させることが難しいため、改質材が適切に着色されない場合もあり、測定精度が悪いという問題がある。 In addition, in Patent Document 2, there is a problem that it is difficult to determine the presence of the modifier liquid from the image of the inner peripheral wall of the penetration hole. Therefore, in Patent Document 2, it is necessary to spray a coloring agent to color the modifier and then measure the inner wall with a camera, but since it is difficult to cause the coloring agent and the modifier to react in the soil, there are cases where the modifier is not properly colored, resulting in a problem of poor measurement accuracy.

本発明は、斯かる実情に鑑み、確実且つ高精度に地盤の改質状態を測定する技術を提供しようとするものである。 In light of this situation, the present invention aims to provide a technology that can reliably and accurately measure the state of ground modification.

上記目的を達成する本発明は、地盤中に導入される土壌の改質材の拡散状態を測定する土壌改質状態測定方法であって、前記改質材が土壌と混在していると推測される場所に形成される縦穴の内部に溜まる改質剤の物性値、又は前記縦穴の内部に溜まる溶媒に前記改質材が溶けることで生成される改質材溶液の物性値を測定する溶液測定工程を備えることを特徴とする、土壌改質状態測定方法である。 The present invention, which achieves the above-mentioned object, is a soil reforming state measurement method for measuring the diffusion state of a soil reforming agent introduced into the ground, characterized in that it includes a solution measurement step for measuring the physical properties of the reforming agent that accumulates inside a vertical hole formed in a place where the reforming agent is assumed to be mixed with the soil, or the physical properties of the reforming agent solution that is generated by dissolving the reforming agent in a solvent that accumulates inside the vertical hole.

上記土壌改質状態測定方法に関連して、前記溶媒が地下水であることを特徴としても良い。 In relation to the above-mentioned soil reform state measurement method, the solvent may be groundwater.

上記土壌改質状態測定方法に関連して、前記縦穴に前記溶媒を供給する溶媒供給工程を備えることを特徴としても良い。 The above-mentioned soil reforming state measurement method may be characterized by including a solvent supplying step for supplying the solvent to the vertical hole.

上記土壌改質状態測定方法に関連して、前記物性値として、前記改質剤又は前記改質材溶液の電気的特性を測定することを特徴としても良い。 In relation to the above-mentioned soil reforming state measurement method, it may be characterized in that the electrical characteristics of the reforming agent or the reforming agent solution are measured as the physical property value.

上記土壌改質状態測定方法に関連して、前記物性値として、前記改質剤又は前記改質材溶液の温度を測定することを特徴としても良い。 In relation to the above-mentioned soil reforming state measurement method, it may be characterized in that the temperature of the reforming agent or the reforming agent solution is measured as the physical property value.

上記土壌改質状態測定方法に関連して、前記物性値として、前記改質剤又は前記改質材溶液のpH値、導電率、酸化還元電位、イオン濃度の少なくともいずれかを測定することを特徴としても良い。 In relation to the above-mentioned soil modification state measurement method, the physical property value may be measured to be at least one of the pH value, electrical conductivity, redox potential, and ion concentration of the modifier or the modifier solution.

上記土壌改質状態測定方法に関連して、前記改質剤又は前記改質材溶液を移動させる溶液移動工程を備え、前記溶液測定工程は、前記溶液移動工程によって移動される前記改質剤又は前記改質材溶液の前記物性値を測定することを特徴としても良い。 In relation to the above-mentioned soil modification state measurement method, a solution transfer process for transferring the modifier or the modifier solution may be provided, and the solution measurement process may be characterized in that it measures the physical property value of the modifier or the modifier solution transferred by the solution transfer process.

上記土壌改質状態測定方法に関連して、前記物性値を測定するセンサと前記改質剤又は前記改質材溶液の接触部分において、前記改質剤又は前記改質材溶液と前記センサを相対移動させることを特徴としても良い。 In relation to the above-mentioned soil reforming state measurement method, a feature may be that the sensor for measuring the physical property value is moved relative to the reforming agent or the reforming agent solution at the contact portion between the sensor and the reforming agent or the reforming agent solution.

上記土壌改質状態測定方法に関連して、共通深度において、前記改質剤又は前記改質材溶液と前記センサとの相対移動を介在させて前記物性値を複数回測定することを特徴としても良い。 In relation to the above-mentioned soil modification state measurement method, the physical property value may be measured multiple times at a common depth by intervening relative movement between the modifier or the modifier solution and the sensor.

上記土壌改質状態測定方法に関連して、前記溶液移動工程では、移動される前記改質剤又は前記改質材溶液をフィルタに通過させるようにし、前記溶液測定工程では、前記フィルタを通過した前記改質剤又は前記改質材溶液の前記物性値を測定することを特徴としても良い。 In relation to the above-mentioned soil reforming state measurement method, the solution transfer process may be characterized in that the modifier or modifier solution being transferred is passed through a filter, and the solution measurement process may be characterized in that the physical property values of the modifier or modifier solution that has passed through the filter are measured.

上記土壌改質状態測定方法に関連して、前記溶液移動工程では、前記改質剤又は前記改質材溶液を地上まで移動させることを特徴としても良い。 In relation to the above-mentioned soil modification state measurement method, the solution moving step may be characterized in that the modifier or the modifier solution is moved to the ground.

上記土壌改質状態測定方法に関連して、前記溶液測定工程では、地上に移動された前記改質剤又は前記改質材溶液の前記物性値を測定することを特徴としても良い。 In relation to the above-mentioned soil modification state measurement method, the solution measurement step may be characterized in that the physical property values of the modifier or the modifier solution that has been moved to the ground are measured.

上記土壌改質状態測定方法に関連して、前記縦穴の内壁を撮像する内壁撮像工程を備えることを特徴としても良い。 The above-mentioned soil reforming state measurement method may be characterized by including an inner wall imaging process for imaging the inner wall of the vertical hole.

上記土壌改質状態測定方法に関連して、前記改質材に、予め、検知用の電解質を含有させるようにし、前記溶液測定工程では、前記電解質のイオン濃度を測定することを特徴としても良い。 In relation to the above-mentioned soil reforming state measurement method, the reforming material may be made to contain an electrolyte for detection in advance, and the solution measurement process may be characterized in that the ion concentration of the electrolyte is measured.

上記目的を達成する本発明は、地盤中に含侵される土壌の改質材の拡散状態を測定する土壌改質状態測定装置であって、前記改質材が土壌と混在していると推測される場所に形成される縦穴に挿入される挿入部材と、前記挿入部材に配置され、前記縦穴の内部に溜まる前記改質剤の物性値又は前記縦穴の内部に溜まる溶媒に前記改質材が溶けることで生成される改質材溶液の物性値を検出するセンサと、を備えることを特徴とする、土壌改質状態測定装置である。 The present invention, which achieves the above-mentioned object, is a soil reforming state measuring device that measures the diffusion state of a soil reforming agent impregnated into the ground, and is characterized by comprising an insertion member that is inserted into a vertical hole formed in a place where the reforming agent is assumed to be mixed with the soil, and a sensor that is placed in the insertion member and detects the physical property values of the reforming agent that accumulates inside the vertical hole or the physical property values of the reforming agent solution that is generated by dissolving the reforming agent in a solvent that accumulates inside the vertical hole.

上記土壌改質状態測定装置に関連して、前記縦穴に前記溶媒を供給する溶媒供給手段を備えることを特徴としても良い。 The soil reforming state measuring device may be characterized by having a solvent supplying means for supplying the solvent to the vertical hole.

上記土壌改質状態測定装置に関連して、前記センサは、前記改質剤又は前記改質材溶液の電気的特性を検知することを特徴としても良い。 In relation to the above soil modification state measuring device, the sensor may be characterized by detecting electrical characteristics of the modifier or the modifier solution.

上記土壌改質状態測定装置に関連して、前記挿入部材に配置され、前記改質剤又は前記改質材溶液の温度を検出する温度検知部を備えることを特徴としても良い。 The soil modification state measuring device may be characterized in that it is provided with a temperature detection unit that is disposed in the insertion member and detects the temperature of the modifier or the modifier solution.

上記土壌改質状態測定装置に関連して、前記センサは、前記改質剤又は前記改質材溶液のpH値、導電率、酸化還元電位、イオン濃度の少なくともいずれかを検知することを特徴としても良い。 In relation to the above soil modification state measuring device, the sensor may be characterized by detecting at least one of the pH value, electrical conductivity, redox potential, and ion concentration of the modifier or the modifier solution.

上記土壌改質状態測定装置に関連して、前記挿入部材に設けられて前記改質剤又は前記改質材溶液を案内する溶液移動路を備え、前記センサは、前記溶液移動路に取り込まれる前記改質剤又は前記改質材溶液の物性値を検出することを特徴としても良い。 In relation to the above soil modification state measuring device, the device may be characterized in that it includes a solution movement path provided in the insertion member to guide the modifier or the modifier solution, and the sensor detects the physical property values of the modifier or the modifier solution taken into the solution movement path.

上記土壌改質状態測定装置に関連して、前記溶液移動路の前記改質剤又は前記改質材溶液を移動させる溶液移動手段を備えることを特徴としても良い。 The soil modification state measuring device may be characterized by having a solution moving means for moving the modifier or the modifier solution in the solution movement path.

上記土壌改質状態測定装置に関連して、前記改質剤又は前記改質材溶液を濾過するフィルタを備え、前記センサは、前記フィルタを通過した前記改質材溶液の前記物性値を検出することを特徴としても良い。 In relation to the above soil modification state measuring device, it may be characterized in that it is provided with a filter for filtering the modifier or the modifier solution, and the sensor detects the physical property value of the modifier solution that has passed through the filter.

上記土壌改質状態測定装置に関連して、前記溶液移動路は、前記改質剤又は前記改質材溶液を地上まで案内することを特徴としても良い。 In relation to the above-mentioned soil modification state measuring device, the solution movement path may be characterized in that it guides the modifier or the modifier solution to the ground.

上記土壌改質状態測定装置に関連して、前記挿入部材に配置され、前記縦穴の内壁を撮像する撮像装置を備えることを特徴としても良い。 The soil reforming state measuring device may be characterized in that it is provided with an imaging device that is disposed in the insertion member and captures an image of the inner wall of the vertical hole.

上記土壌改質状態測定装置に関連して、前記挿入部材は、前記センサが配置されるセンサ収容部、及び、前記撮像装置が配置される撮像装置収容部を有しており、前記センサ収容部及び撮像装置収容部が、分離自在となっていることを特徴としても良い。 In relation to the above soil reforming state measuring device, the insertion member may have a sensor housing section in which the sensor is disposed, and an imaging device housing section in which the imaging device is disposed, and the sensor housing section and the imaging device housing section may be characterized in that they are freely separable.

上記土壌改質状態測定装置に関連して、前記撮像装置収容部に対して、前記センサ収容部が上方に配置されることを特徴としても良い。 The soil reforming state measuring device may be characterized in that the sensor housing is disposed above the imaging device housing.

上記目的を達成する本発明は、地盤中に含侵される土壌の改質材の混在状態を測定する土壌改質状態測定装置であって、前記改質材が混在していると推測される場所に形成される縦穴に挿入され、前記縦穴の内部に溜まる前記改質剤又は前記縦穴の内部に溜まる溶媒に前記改質材が溶けることで生成される改質材溶液を地上に汲み上げる汲み上げ手段と、前記地上に配置され、前記汲み上げ手段によって地上に汲み上げられる前記改質剤又は前記改質材溶液の物性値を検出するセンサと、を備えることを特徴とする、土壌改質状態測定装置である。 The present invention, which achieves the above-mentioned object, is a soil reforming state measuring device that measures the mixed state of soil modifiers impregnated in the ground, and is characterized by comprising: a pumping means that is inserted into a vertical hole formed in a place where the modifier is assumed to be mixed, and pumps up to the ground the modifier that accumulates inside the vertical hole or a modifier solution that is generated by dissolving the modifier in a solvent that accumulates inside the vertical hole; and a sensor that is placed on the ground and detects the physical property values of the modifier or the modifier solution that is pumped up to the ground by the pumping means.

本発明によれば、確実且つ高精度に地盤の改質状態を測定できるという優れた効果を奏し得る。 The present invention has the excellent effect of being able to measure the state of ground modification reliably and with high accuracy.

本発明の実施形態に係る土壌改質状態測定装置の全体構成を示す正面図である。1 is a front view showing the overall configuration of a soil reforming state measuring device according to an embodiment of the present invention. 同土壌改質状態測定装置の挿入部材を拡大して示す(A)正面図、(B)正面断面図である。2A is a front view showing an enlarged view of an insertion member of the soil reformation state measuring device, and FIG. 2B is a front cross-sectional view showing the same. (A)~(D)は本発明の実施形態に係る土壌改質状態測定方法を示す工程図である。1A to 1D are process diagrams showing a method for measuring a soil reformed state according to an embodiment of the present invention. 同土壌改質状態測定装置の制御装置の機能構成を示すブロック図である。2 is a block diagram showing the functional configuration of a control device of the soil modification state measuring device. FIG. 同土壌改質状態測定方法のフローチャートである。2 is a flowchart of the soil reformation state measuring method. (A)は測定中の同挿入部材の動作を示す正面断面図であり、(B)は測定されたデータのサンプルを示すグラフである。1A is a front cross-sectional view showing the operation of the insert during measurement, and FIG. 1B is a graph showing a sample of the measured data. 同土壌改質状態測定方法によって測定されたデータのサンプルを示すグラフである。1 is a graph showing sample data measured by the soil reformation state measuring method. 同土壌改質状態測定装置の挿入部材の変形例を拡大して示す正面断面図である。13 is an enlarged front cross-sectional view showing a modified example of the insertion member of the soil reformation state measuring device. FIG. 同土壌改質状態測定装置の挿入部材の変形例を拡大して示す(A)正面図、(B)正面断面図である。1A is a front view showing an enlarged view of a modified example of the insertion member of the soil reformation state measuring device, and FIG. (A)は測定中の変形例に係る同挿入部材の動作を示す正面断面図であり、(B)は測定されたデータのサンプルを示すグラフである。13A is a front cross-sectional view showing the operation of the insertion member according to the modified example during measurement, and FIG. 13B is a graph showing a sample of the measured data. 変形例に係る土壌改質状態測定装置の全体構成を示す正面図である。FIG. 13 is a front view showing the overall configuration of a soil modification state measuring device according to a modified example.

以下、本発明の実施の形態について添付図面を参照して説明する。 The following describes an embodiment of the present invention with reference to the attached drawings.

<土壌改質状態測定装置の全体構造> <Overall structure of the soil reformation status measuring device>

図1に、本発明の実施形態に係る土壌改質状態測定装置1の全体構造を示す。この土壌改質状態測定装置1は、地盤に縦穴5を掘削する掘削装置(挿入装置)10と、縦穴5内に挿入される挿入部材20と、挿入部材20に設けられるセンサ50と、挿入部材20に設けられる温度検知部58と、挿入部材20に設けられる撮像装置65を備える。なお、挿入部材20は、互いに連結される複数の挿入ロッド12の下端に固定される。掘削装置10によって挿入ロッド12を上下動させることで、挿入部材20が縦穴5内の上下方向に沿って進退する。つまり、掘削装置10は、挿入部材20を上下動させる移動機構を兼ねる。 Figure 1 shows the overall structure of a soil reforming state measuring device 1 according to an embodiment of the present invention. This soil reforming state measuring device 1 includes an excavation device (insertion device) 10 that excavates a vertical hole 5 in the ground, an insertion member 20 that is inserted into the vertical hole 5, a sensor 50 provided on the insertion member 20, a temperature detection unit 58 provided on the insertion member 20, and an imaging device 65 provided on the insertion member 20. The insertion member 20 is fixed to the lower end of a plurality of insertion rods 12 that are connected to each other. By moving the insertion rods 12 up and down using the excavation device 10, the insertion member 20 advances and retreats in the vertical direction within the vertical hole 5. In other words, the excavation device 10 also serves as a moving mechanism that moves the insertion member 20 up and down.

土壌改質状態測定装置1は、更に、挿入部材20の吐出口30Aを経由させて縦穴5に溶媒となる水を供給する溶媒供給路30を有する。地上には、溶媒タンク32が設けられており、溶媒供給路30は、吐出口30Aと溶媒タンク32を繋ぐ。なお、溶媒供給路30の途中には、溶媒移送手段となる送液ポンプ33が配置されており、溶媒タンク32内の溶媒(水)を吸引して、吐出口30Aから吐出するようになっている。なお、溶媒移送手段は、送液ポンプ33に限定されず、溶媒タンク32の内部空間の圧力を制御する圧力制御装置(コンプレッサ)を設けるようにし、その内圧制御によって、溶媒を溶媒供給路30側に送液することもできる。溶媒供給路30の途中に制御弁を設けることで、溶媒の送液状態を制御しても良い。 The soil reforming state measuring device 1 further has a solvent supply path 30 that supplies water as a solvent to the vertical hole 5 via the outlet 30A of the insertion member 20. A solvent tank 32 is provided on the ground, and the solvent supply path 30 connects the outlet 30A and the solvent tank 32. A liquid delivery pump 33 that serves as a solvent transport means is provided in the middle of the solvent supply path 30, and the solvent (water) in the solvent tank 32 is sucked in and discharged from the outlet 30A. The solvent transport means is not limited to the liquid delivery pump 33, and a pressure control device (compressor) that controls the pressure in the internal space of the solvent tank 32 can be provided, and the solvent can be delivered to the solvent supply path 30 side by controlling the internal pressure. A control valve can be provided in the middle of the solvent supply path 30 to control the solvent delivery state.

縦穴5内には、土壌の改質材が溶媒となる水に溶けることで生成される改質材溶液Yが貯留される。溶媒となる水は、地上から供給される場合の他、地中に予め存在する地下水であっても良い。 The vertical hole 5 stores a modifier solution Y, which is generated by dissolving the soil modifier in the water that acts as a solvent. The water that acts as the solvent may be supplied from above ground, or it may be groundwater that is already present underground.

挿入部材20には、溶液移動路40が設けられる(図2参照)。溶液移動路40の一端(下端)は、挿入部材20の吸入口40Aに繋がる。結果、この溶液移動路40の内部には、縦穴5内に存在する改質材溶液Yが流れ込む。地上には、溶液タンク42が設けられる。溶液移動路40は、挿入部材20から地上に向かって延長されて、その他端が溶液タンク42に繋がる。溶液タンク42には、溶液移動手段となる圧力制御装置43が接続され、溶液タンク42内の内圧を制御する。本実施形態では、圧力制御装置43は例えば真空ポンプであり、溶液タンク42内の気体を排気して内圧を下げると、縦穴5内の改質材溶液Yが溶液移動路40に吸引されて地上まで吸い上げられて溶液タンク42に流れ込む。一方、圧力制御装置43が、溶液タンク42内の排気を停止して内圧を高めると、縦穴5内の改質材溶液Yの吸い上げが停止される。圧力制御装置43は、溶液タンク42内を加圧して、吸引した改質材溶液Yを地下に向かって逆流させることもできる。なお、ここでは溶液移動手段が圧力制御装置43の場合を例示したが、送液ポンプであっても良い。溶液移動路40の途中に制御弁を設けることで、改質材溶液Yの送液状態(移動状態)を制御しても良い。 The insertion member 20 is provided with a solution movement path 40 (see FIG. 2). One end (lower end) of the solution movement path 40 is connected to the suction port 40A of the insertion member 20. As a result, the modifier solution Y present in the vertical hole 5 flows into the inside of this solution movement path 40. A solution tank 42 is provided on the ground. The solution movement path 40 is extended from the insertion member 20 toward the ground, and the other end is connected to the solution tank 42. A pressure control device 43, which serves as a solution movement means, is connected to the solution tank 42 to control the internal pressure in the solution tank 42. In this embodiment, the pressure control device 43 is, for example, a vacuum pump, and when the gas in the solution tank 42 is exhausted to lower the internal pressure, the modifier solution Y in the vertical hole 5 is sucked into the solution movement path 40, sucked up to the ground, and flows into the solution tank 42. On the other hand, when the pressure control device 43 stops exhausting the solution tank 42 and increases the internal pressure, the suction of the modifier solution Y in the vertical hole 5 is stopped. The pressure control device 43 can also pressurize the solution tank 42 to cause the aspirated modifier solution Y to flow back underground. Although the solution moving means is illustrated here as a pressure control device 43, a liquid delivery pump may also be used. The delivery state (movement state) of the modifier solution Y may be controlled by providing a control valve midway along the solution movement path 40.

更に土壌改質状態測定装置1は、地上に配置される制御装置70を有する。この制御装置70は、コントローラ71及びパーソナルコンピュータ80を有する。コントローラ71には、検知配線72を経由して、センサ50及び温度検知部58の検知信号(検知電流)が入力される。コントローラ71には、映像配線74を経由して撮像装置65からの映像信号が入力される。また、コントローラ71は、位置情報配線76を介して、掘削装置10による挿入部材20の地上からの挿入距離(挿入深度)に関する情報を受信する。コントローラ71は、圧力制御装置43や送液ポンプ33の他、特に図示しない各種制御弁を制御することができる。コントローラ71には、ディスプレイを有するパーソナルコンピュータ80が接続される。なお、ここではコントローラ71とパーソナルコンピュータ80を備える構成を例示しているが、単一の計算機が、コントローラ71とパーソナルコンピュータ80を兼ねることもできる。もちろん、複数の計算機に分散させることもできる。 The soil reforming state measuring device 1 further includes a control device 70 arranged on the ground. The control device 70 includes a controller 71 and a personal computer 80. The controller 71 receives detection signals (detection currents) from the sensor 50 and the temperature detector 58 via the detection wiring 72. The controller 71 receives a video signal from the imaging device 65 via the video wiring 74. The controller 71 also receives information on the insertion distance (insertion depth) of the insertion member 20 from the ground by the drilling device 10 via the position information wiring 76. The controller 71 can control the pressure control device 43, the liquid delivery pump 33, and various control valves (not shown). The controller 71 is connected to a personal computer 80 having a display. Note that, although a configuration including the controller 71 and the personal computer 80 is illustrated here, a single computer can also function as both the controller 71 and the personal computer 80. Of course, they can also be distributed among multiple computers.

制御装置70の一部であるコントローラ71は、特に図示しないいわゆる計算機を内蔵しており、詳細にはCPU、RAM、ROM、入出力インターフェース、バス等を備える。CPUは、いわゆる中央演算処理装置であり、各種プログラムが実行されて制御装置70の各種機能を実現する。RAMは、ランダム・アクセス・メモリであり、CPUの作業領域として使用される。ROMはリード・オンリー・メモリであり、CPUで実行される基本OSや各種プログラム(例えば、土壌改質状態測定プログラム)を記憶する。入出力インターフェースには、入力キーや、パーソナルコンピュータ80のキーボードやマウスの操作情報が入力される。入出力インターフェースには、記憶装置を動作させる電源や、検知配線72、映像配線74、圧力制御装置43、送液ポンプ33、パーソナルコンピュータ80との間で制御信号が入出力される。バスは、CPU、RAM、ROM、入力装置、入出力インターフェースなどを一体的に接続して通信を行う配線となる。ROMに記憶された基本OSや土壌改質状態測定プログラムが、CPUによって実行されると、土壌改質状態測定装置1による土壌改質状態測定が実施される。 The controller 71, which is a part of the control device 70, has a built-in so-called calculator (not shown), and more specifically, includes a CPU, RAM, ROM, an input/output interface, a bus, etc. The CPU is a so-called central processing unit, and various programs are executed to realize various functions of the control device 70. The RAM is a random access memory, and is used as a working area for the CPU. The ROM is a read-only memory, and stores the basic OS and various programs (e.g., a soil reforming state measurement program) executed by the CPU. The input/output interface receives operation information from the input keys, the keyboard and mouse of the personal computer 80. The input/output interface receives and outputs control signals between the power supply that operates the storage device, the detection wiring 72, the video wiring 74, the pressure control device 43, the liquid delivery pump 33, and the personal computer 80. The bus is a wiring that integrally connects the CPU, RAM, ROM, input device, input/output interface, etc. to communicate. When the basic OS and soil reforming state measurement program stored in the ROM are executed by the CPU, soil reforming state measurement is performed by the soil reforming state measurement device 1.

<挿入部材の詳細構造> <Detailed structure of the insert>

図2に、挿入部材20の詳細構造を示す。挿入部材20は、センサ50が収容されるセンサ収容部22、及び、撮像装置65が収容される撮像装置収容部60を有する。センサ収容部22と撮像装置収容部60は、ねじによる締結構造によって、着脱自在に連結されている。 Figure 2 shows the detailed structure of the insertion member 20. The insertion member 20 has a sensor housing section 22 that houses the sensor 50, and an imaging device housing section 60 that houses the imaging device 65. The sensor housing section 22 and the imaging device housing section 60 are detachably connected by a screw fastening structure.

センサ収容部22は、円筒状のセンサ側筐体24を有する。センサ側筐体24の上端外周には雄ねじ部24Aが形成され、挿入ロッド12(図1参照)の下端に形成される雌ねじ部と螺合する。センサ側筐体24の下端内周には雌ねじ部24Bが形成され、撮像装置収容部60と螺合する。センサ側筐体24の周面には吐出口30Aが開口する。センサ側筐体24の内部には、溶媒供給路30が収容されており、その一端が吐出口30Aに連通する。溶媒供給路30の他端は、センサ側筐体24の上端側に延びてロッド12内まで延長される。なお、この溶媒供給路30の他端は、地上の溶媒タンク32内の溶媒(水)に達する。結果、溶媒タンク32内の溶媒(水)が、溶媒供給路30を経由して吐出口30Aから縦穴5内に吐出される。なお、ここではセンサ収容部22に、溶媒供給路30及び吐出口30Aを設ける場合を例示したが、センサ収容部22から分離した別部材(専用の溶媒供給路収容部)の筐体(専用の溶媒供給側筐体)に設けるようにしても良い。 The sensor housing 22 has a cylindrical sensor side housing 24. A male thread 24A is formed on the outer periphery of the upper end of the sensor side housing 24, which screws into a female thread formed at the lower end of the insertion rod 12 (see FIG. 1). A female thread 24B is formed on the inner periphery of the lower end of the sensor side housing 24, which screws into the imaging device housing 60. An outlet 30A opens on the periphery of the sensor side housing 24. A solvent supply path 30 is housed inside the sensor side housing 24, and one end of the path is connected to the outlet 30A. The other end of the solvent supply path 30 extends to the upper end side of the sensor side housing 24 and into the rod 12. The other end of the solvent supply path 30 reaches the solvent (water) in the solvent tank 32 on the ground. As a result, the solvent (water) in the solvent tank 32 is discharged from the outlet 30A into the vertical hole 5 via the solvent supply path 30. In this example, the solvent supply path 30 and the discharge port 30A are provided in the sensor housing 22, but they may be provided in a housing (dedicated solvent supply side housing) of a separate member (dedicated solvent supply path housing) separated from the sensor housing 22.

センサ側筐体24の周面には吸入口40Aが開口する。センサ側筐体24の内部には、溶液移動路40が収容されており、その一端が吸入口40Aに連通する。溶液移動路40の他端は、センサ側筐体24の上端側に延びて挿入ロッド12内まで延長される。なお、溶液移動路40の他端は、地上の溶液タンク42に到達する。結果、縦穴5内に溜まる改質材溶液Yは、吸入口40Aから吸引され、溶液移動路40を経由して溶液タンク42に排出される。 An intake port 40A opens on the periphery of the sensor side housing 24. A solution movement path 40 is housed inside the sensor side housing 24, and one end of the path is connected to the intake port 40A. The other end of the solution movement path 40 extends to the upper end side of the sensor side housing 24 and into the insertion rod 12. The other end of the solution movement path 40 reaches a solution tank 42 on the ground. As a result, the modifier solution Y that accumulates in the vertical hole 5 is sucked in from the intake port 40A and discharged into the solution tank 42 via the solution movement path 40.

溶液移動路40の途中(ここでは吸入口40A)には、フィルタ44が配置される。このフィルタ44は、改質材溶液Yに含まれる砂利や土等をろ過する。更に溶液移動路40の途中において、フィルタ44よりも下流側(ここでは吸入口40Aを上流側と定義する)には、他の流路よりも拡張されるバッファ空間40Bが形成される。このバッファ空間40Bを画定する周壁には、センサ50及び温度検知部58が配置され、バッファ空間40B内を通過する改質材溶液Yと接触して、その物性値及び温度を測定する。 A filter 44 is placed in the middle of the solution flow path 40 (here, at the intake port 40A). This filter 44 filters out gravel, soil, etc. contained in the modifier solution Y. Furthermore, in the middle of the solution flow path 40, downstream of the filter 44 (here, the intake port 40A is defined as the upstream side), a buffer space 40B is formed that is larger than the other flow paths. A sensor 50 and a temperature detection unit 58 are placed on the peripheral wall that defines this buffer space 40B, and come into contact with the modifier solution Y passing through the buffer space 40B to measure its physical properties and temperature.

本実施形態のセンサ50はpH計となっており、感応電極51及び比較電極52を有する。感応電極51は、ここではガラス電極となっており、ガラス応答膜によって改質材溶液Yの水素イオンに選択的に応答して、改質材溶液YのpH値に相当する起電力(電位)を出力する。比較電極52は、改質材溶液YのpH値に依存しない安定的な電位を出力する。結果、センサ50は、感応電極51と比較電極52の電位差によってpH値を測定可能となる。なお、温度検知部58は、改質材溶液の温度を測定する。感応電極51に発生する起電力(電位)は、改質材溶液Yの温度によって変化することから、測定される温度を利用して起電力(電位)を補正(補償)する。センサ50及び温度検知部58の検知信号(検知電流・検知電位)は、検知配線72を経由して制御装置70に伝達される。 The sensor 50 in this embodiment is a pH meter and has a sensitive electrode 51 and a comparison electrode 52. The sensitive electrode 51 is a glass electrode, which selectively responds to hydrogen ions in the modifier solution Y by a glass response membrane and outputs an electromotive force (electric potential) corresponding to the pH value of the modifier solution Y. The comparison electrode 52 outputs a stable electric potential that is not dependent on the pH value of the modifier solution Y. As a result, the sensor 50 can measure the pH value based on the electric potential difference between the sensitive electrode 51 and the comparison electrode 52. The temperature detection unit 58 measures the temperature of the modifier solution. Since the electromotive force (electric potential) generated in the sensitive electrode 51 changes depending on the temperature of the modifier solution Y, the electromotive force (electric potential) is corrected (compensated) using the measured temperature. The detection signals (detection current and detection electric potential) of the sensor 50 and the temperature detection unit 58 are transmitted to the control device 70 via the detection wiring 72.

なお、本実施形態ではセンサ50がpH計となる場合を例示したが、本発明はこれに限定されない。センサ50は、改質材溶液Yの電気的特性を検知できるものであれば良い。また、センサ50は、改質材溶液の物性値を検知できれば良い。例えばセンサ50は、導電率計、酸化還元電位計、イオン濃度計などが好ましい。 In this embodiment, the sensor 50 is a pH meter, but the present invention is not limited to this. The sensor 50 may be any sensor capable of detecting the electrical characteristics of the modifier solution Y. The sensor 50 may be any sensor capable of detecting the physical properties of the modifier solution. For example, the sensor 50 may be a conductivity meter, an oxidation-reduction potentiometer, an ion concentration meter, or the like.

撮像装置収容部60は、円筒状の撮像装置側筐体64を有する。撮像装置側筐体64の上端外周には雄ねじ部64Aが形成され、センサ側筐体24の下端に形成される雌ねじ部24Bと螺合する。撮像装置側筐体64の下端内周には雌ねじ部64Bが形成され、円錐形の先端コーン69と螺合する。撮像装置側筐体64の周面には撮像口65Aが開口する。撮像装置側筐体64の内部には、撮像装置65が固定されており、その撮像レンズが撮像口65Aに臨む。結果、撮像装置65が、縦穴5の内壁を撮像できる。撮像装置65の映像信号は、映像配線74を経由して制御装置70に伝達される。 The imaging device housing 60 has a cylindrical imaging device side housing 64. A male thread 64A is formed on the outer periphery of the upper end of the imaging device side housing 64, which screws into a female thread 24B formed on the lower end of the sensor side housing 24. A female thread 64B is formed on the inner periphery of the lower end of the imaging device side housing 64, which screws into a conical tip cone 69. An imaging port 65A opens on the peripheral surface of the imaging device side housing 64. An imaging device 65 is fixed inside the imaging device side housing 64, and its imaging lens faces the imaging port 65A. As a result, the imaging device 65 can capture an image of the inner wall of the vertical hole 5. The video signal of the imaging device 65 is transmitted to the control device 70 via the video wiring 74.

この挿入部材20では、センサ収容部22が上方、撮像装置収容部60が下方に配置される。即ち、センサ50の縦穴5内の移動範囲よりも、撮像装置65の移動範囲の方が広い。例えば、センサ50で測定される改質材溶液の物性値に誤差が大きい場合や、物性値に異常値が含まれる場合は、それよりも広範囲の撮像装置65の内壁映像によって、その誤差等の要因を目視によって分析できる。 In this insertion member 20, the sensor housing 22 is located at the top and the imaging device housing 60 is located at the bottom. That is, the movement range of the imaging device 65 is wider than the movement range of the sensor 50 inside the vertical hole 5. For example, if there is a large error in the physical property values of the modifier solution measured by the sensor 50 or if the physical property values include abnormal values, the cause of the error etc. can be visually analyzed using the wider range of the inner wall image of the imaging device 65.

また、先端コーン69を備えているので、掘削装置10によって挿入部材20を土壌に貫入することで、縦穴5自体を同時に掘削することができる。つまり、この挿入部材20は、縦穴5を掘削する掘削工程も同時に実施できる。 In addition, since it is equipped with a tip cone 69, the vertical hole 5 itself can be excavated at the same time by penetrating the insertion member 20 into the soil using the excavation device 10. In other words, the insertion member 20 can also simultaneously perform the excavation process of excavating the vertical hole 5.

なお、撮像装置収容部60を省略する場合は、先端コーン69を、センサ側筐体24の雌ねじ部24Bに螺合させることもできる。 If the imaging device housing 60 is omitted, the tip cone 69 can be screwed into the female threaded portion 24B of the sensor side housing 24.

<土壌改質状態測定方法> <Method for measuring soil reform status>

次に、図3の外観模式図、図4の制御装置70における測定プログラムの機能構成ブロック、図5の測定フロー、図6及び図7の測定データ値等を参照して、土壌改質状態の測定手順を説明する。 Next, the procedure for measuring the soil reforming state will be explained with reference to the schematic diagram of the external appearance in FIG. 3, the functional configuration block of the measurement program in the control device 70 in FIG. 4, the measurement flow in FIG. 5, and the measurement data values in FIG. 6 and FIG. 7.

まず、図3(A)に示すように、土壌改質を行う前の状態において、将来、土壌改質が行われる予定範囲Pの内側、かつ、その改質有効範囲の確認が必要となる位置に、掘削装置10および挿入ロッド12等を利用して挿入部材20を挿入することで縦穴5を掘削する(測定用縦穴掘削工程S112)。この縦穴5は、地盤に改質材を導入する改質中心軸Cから離れた場所となる。なお、ここでは挿入部材20の挿入と同時に縦穴5を掘削する場合を例示するが、縦穴5の掘削方法は特に限定されず、他の掘削装置で別途掘削してもよい。 First, as shown in FIG. 3(A), before soil reforming, a vertical hole 5 is excavated by inserting an insertion member 20 using an excavation device 10 and an insertion rod 12, etc., inside the planned area P where soil reforming will be performed in the future and at a position where confirmation of the effective reforming area is required (measurement vertical hole excavation step S112). This vertical hole 5 is located away from the reforming central axis C where the reforming material is introduced into the ground. Note that, although an example is shown here of excavating the vertical hole 5 at the same time as inserting the insertion member 20, the method of excavating the vertical hole 5 is not particularly limited, and it may be excavated separately using another excavation device.

次に、図3(B)に示すように、掘削装置10および挿入ロッド12等を利用して、挿入部材20を縦穴5内に挿入する(挿入部材挿入工程S114)。なお、既に述べたように、本実施形態では、測定用縦穴掘削工程S112と同時に、挿入部材挿入工程S114が完了している。なお、測定用縦穴掘削工程S112又は挿入部材挿入工程S114の事前準備として、図1に示すように、挿入部材20の最大深度に対応可能な複数の挿入ロッド12の内部に、予め、検知配線72、映像配線74、溶媒供給路30、溶液移動路40を挿入しておき、この挿入ロッド12を継ぎ足しながら、挿入部材20を地中に貫入させていく。 Next, as shown in FIG. 3B, the drilling device 10 and the insertion rod 12 are used to insert the insertion member 20 into the vertical hole 5 (insertion member insertion step S114). As already mentioned, in this embodiment, the insertion member insertion step S114 is completed at the same time as the measurement vertical hole drilling step S112. As a preliminary preparation for the measurement vertical hole drilling step S112 or the insertion member insertion step S114, as shown in FIG. 1, the detection wiring 72, the video wiring 74, the solvent supply path 30, and the solution movement path 40 are inserted in advance into the multiple insertion rods 12 that can correspond to the maximum depth of the insertion member 20, and the insertion member 20 is penetrated into the ground while the insertion rods 12 are added.

その後、土壌改質状態測定装置1は、溶媒となる水を、挿入部材20の吐出口30Aから吐出して、縦穴5内を溶媒で満たす(溶媒注入工程S116)。制御装置70における溶液注入処理部710は、送液ポンプ33を制御して、溶媒タンク32内の溶媒(水)を吸引して、吐出口30Aから吐出させる。なお、地下水が豊富な地盤であって、掘削後の縦穴5内に地下水が自ずと満たされる場合は、この溶媒注入工程を省略しても良い。 Then, the soil reforming state measuring device 1 discharges water, which serves as a solvent, from the outlet 30A of the insertion member 20 to fill the vertical hole 5 with the solvent (solvent injection step S116). The solution injection processing unit 710 in the control device 70 controls the liquid delivery pump 33 to suck up the solvent (water) in the solvent tank 32 and discharge it from the outlet 30A. Note that if the ground is rich in groundwater and the groundwater naturally fills the vertical hole 5 after excavation, this solvent injection step may be omitted.

必要に応じて、この状態でしばらく待機し、土壌の成分が縦穴5内の溶媒(水)に十分に溶け出させることで、改質前溶液Zの物性値が安定した状態となるようにする。 If necessary, wait for a while in this state to allow the soil components to fully dissolve into the solvent (water) in the vertical hole 5 so that the physical properties of the pre-modified solution Z become stable.

次に、最深位置に配置される挿入部材20を連続的又は段階的に上昇させながら、複数個所の測定深度において、センサ50及び温度検知部58を利用して、土壌の成分が溶け出した改質前溶液Zの物性値(ここではpH値)を測定する(溶液移動工程及び事前測定工程S118)。なお、この際に撮像装置65によって縦穴5の内壁の撮像も実行する。 Next, the insertion member 20, which is located at the deepest position, is raised continuously or stepwise, and the physical property value (here, pH value) of the pre-modified solution Z, into which the soil components have dissolved, is measured at multiple measurement depths using the sensor 50 and temperature detection unit 58 (solution transfer process and pre-measurement process S118). At this time, the imager 65 also captures an image of the inner wall of the vertical hole 5.

より詳細に、図6(A)に示すように、特定の深度(例えば深度-16.0m)においてpH値を測定する場合、制御装置70の深度情報保存部730は、掘削装置10からの信号に基づいて、挿入部材20が正しい深度(-16.0m)に位置するか否かを判定する。なお、必要に応じて、掘削装置10を制御して挿入部材20を正しい深度に再度位置決めしても良い。その後、制御装置70における溶液移動処理部720は、溶液移動手段となる圧力制御装置43を制御して、溶液タンク42内の気体を排気する。これにより、深度-16.0mmに相応する水圧を有する改質前溶液Zが、吸入口40Aを介してバッファ空間40Bに流れ込み、溶液移動路40に沿って上昇する(点線矢印参照/溶液移動工程)。結果、センサ50と改質前溶液Zの接触部分で、溶液とセンサ50が相対移動する。 In more detail, as shown in FIG. 6(A), when measuring the pH value at a specific depth (for example, a depth of -16.0 m), the depth information storage unit 730 of the control device 70 judges whether the insertion member 20 is located at the correct depth (-16.0 m) based on a signal from the drilling device 10. If necessary, the drilling device 10 may be controlled to reposition the insertion member 20 at the correct depth. After that, the solution movement processing unit 720 in the control device 70 controls the pressure control device 43, which serves as the solution movement means, to exhaust the gas in the solution tank 42. As a result, the pre-modified solution Z having a water pressure corresponding to a depth of -16.0 mm flows into the buffer space 40B through the intake port 40A and rises along the solution movement path 40 (see dotted arrow/solution movement process). As a result, the solution and the sensor 50 move relative to each other at the contact portion between the sensor 50 and the pre-modified solution Z.

制御装置70の測定処理部740は、バッファ空間40B内で改質前溶液Zの移動を伴いつつ、複数回に亘って溶液のpHを測定することで、図6(B)のように、特定深度(-16.0m)における複数のpH値が検知される。測定処理部740は、この複数pH値に基づいて、その特定深度の最終的なpH値を決定する。なお、最終的なpH値の決定方法は、これらの複数の全てのpH値の平均値を採用しても良いが、他にも、複数のpH値からノイズ成分(例えば最大値側及び最小値側のデータ又はデータ群)を除去した残データを利用して、平均値等を算出しても良く、その他の手法を採用してもよい。いずれにしろ、深度-16.0mの改質前溶液Zを吸引して、センサ50と相対移動させながら、その改質前溶液ZのpH値を複数回測定することで、測定誤差を低減させることが好ましい。 The measurement processing unit 740 of the control device 70 measures the pH of the solution multiple times while the pre-modified solution Z moves within the buffer space 40B, and multiple pH values at a specific depth (-16.0 m) are detected as shown in FIG. 6 (B). The measurement processing unit 740 determines the final pH value at the specific depth based on the multiple pH values. The final pH value may be determined by using the average value of all of these multiple pH values, or by using the remaining data obtained by removing noise components (e.g., data or data groups on the maximum and minimum sides) from the multiple pH values to calculate the average value, or by using other methods. In any case, it is preferable to reduce measurement errors by aspirating the pre-modified solution Z at a depth of -16.0 m and measuring the pH value of the pre-modified solution Z multiple times while moving it relative to the sensor 50.

以上結果、例えば、図7の白丸に示されるように、複数の深度(ここでは2.0m毎の深度)において、改質前溶液Zの土壌のpH値が測定される。 As a result of the above, for example, as shown by the white circles in Figure 7, the pH value of the soil of the pre-modified solution Z is measured at multiple depths (here, at depths of 2.0 m each).

その後、図3(C)に示すように、改質中心軸Cを掘削して改質用縦穴200を掘削し、改質材を噴射するジェットノズルを挿入して、改質中心軸Cを起点として放射状に改質材を高圧噴射する(地盤改質工程S120)。結果、ジェット噴射の勢いによって改質材と土壌が撹拌混合されて、改質材によって地盤が改良された範囲Qが形成される。なお、本実施形態では、地盤の改良範囲Qが円柱状となる場合を例示したが、本発明はこれに限定されず、扇状や放射状等、様々な形状にできる。 After that, as shown in FIG. 3(C), the central axis C of the modification is excavated to excavate a vertical hole 200 for modification, a jet nozzle for spraying the modification material is inserted, and the modification material is sprayed at high pressure radially from the central axis C of the modification (ground modification process S120). As a result, the force of the jet spray stirs and mixes the modification material and the soil, forming an area Q where the ground has been improved by the modification material. Note that, although the present embodiment illustrates a case where the improvement area Q of the ground is cylindrical, the present invention is not limited to this, and various shapes such as a fan shape or a radial shape are possible.

次いで、図3(D)に示すように、土壌改質状態測定装置1は、掘削装置10や挿入ロッド12等を利用して、再度、挿入部材20を縦穴5内に挿入する(挿入部材挿入工程S122)。なお、地盤改質工程S120によって、縦穴5が消失している場合であっても、挿入部材20の先端コーン69によって、その挿入と同時に縦穴5を新たに掘削できる。なお、本発明はこれに限定されず、挿入部材挿入工程S122の前に、再度、別の装置によって測定用の縦穴5を掘削しても良い。 Next, as shown in FIG. 3(D), the soil reforming state measuring device 1 uses the excavation device 10 and the insertion rod 12, etc. to insert the insertion member 20 into the vertical hole 5 again (insertion member inserting step S122). Note that even if the vertical hole 5 has disappeared due to the ground reforming step S120, the tip cone 69 of the insertion member 20 can be used to excavate a new vertical hole 5 at the same time as the insertion. Note that the present invention is not limited to this, and a vertical hole 5 for measurement may be excavated again using another device before the insertion member inserting step S122.

その後、土壌改質状態測定装置1は、再度、溶媒となる水を、挿入部材20の吐出口30Aを吐出して、縦穴5内を溶媒で満たす(溶媒注入工程S124)。なお、この溶媒注入工程S124は、以下(1)又は(2)の場合に省略できる。
(1)液体状の改質剤自体が縦穴5内に十分に満たされている場合。
(2)溶媒となりうる地下水が豊富な地盤であって、掘削後の縦穴5内に地下水が自ずと満たされることで、ジェット噴射された改質材の少なくとも一部の成分がこの地下水(溶媒)に溶け出して改質材溶液が生成される場合。
Thereafter, the soil modification state measuring device 1 again discharges water as a solvent from the outlet 30A of the insertion member 20 to fill the vertical hole 5 with the solvent (solvent injection step S124). Note that this solvent injection step S124 can be omitted in the following cases (1) or (2).
(1) When the liquid modifier itself is sufficiently filled in the vertical hole 5.
(2) The ground is rich in groundwater that can act as a solvent, and the groundwater naturally fills the vertical hole 5 after excavation, causing at least some of the components of the jetted modifier to dissolve in the groundwater (solvent) and produce a modifier solution.

一方で、例えば改質剤の粘性が高い場合や、地下水に溶け出しにくい改質剤の場合は、改質剤が溶けやすい専用溶媒を挿入部材20の吐出口30Aを吐出して、改質材溶液で満たすことの好ましい。 On the other hand, for example, if the modifier has high viscosity or is difficult to dissolve in groundwater, it is preferable to eject a dedicated solvent in which the modifier is easily dissolved from the outlet 30A of the insertion member 20 and fill it with the modifier solution.

次に、最深位置に配置される挿入部材20を連続的又は段階的に上昇させながら、複数個所の測定深度において、センサ50及び温度検知部58を利用して、改質剤そのもの又は改質材が水に溶け出した改質材溶液(以下、これらを総称して改質材溶液等Yと称する)の物性値(ここではpH値)を測定する(溶液移動及び事後測定工程S126)。なお、この際に、撮像装置65によって、縦穴5の内壁の撮像も実行する。 Next, while the insertion member 20 located at the deepest position is raised continuously or stepwise, the physical property value (here, pH value) of the modifier itself or the modifier solution in which the modifier has dissolved in water (hereinafter, these are collectively referred to as modifier solution Y) is measured at multiple measurement depths using the sensor 50 and temperature detection unit 58 (solution movement and post-measurement step S126). At this time, the imager 65 also captures an image of the inner wall of the vertical hole 5.

事後測定工程S126において、図6(A)に示すように、特定の深度(例えば深度-16.0m)においてpH値を測定する場合、制御装置70の深度情報保存部730は、掘削装置10からの信号に基づいて挿入部材20が正しい深度(-16.0m)に位置するか否かを判定する。なお、必要に応じて、掘削装置10を制御して挿入部材20を正しい深度に位置決めしても良い。その後、制御装置70における溶液移動処理部720は、溶液移動手段となる圧力制御装置43を制御して、溶液タンク42内の気体を排気する。これにより、深度-16.0mmに相応する水圧を有する改質材溶液等Yが、吸入口40Aを介してバッファ空間40Bに流れ込み、溶液移動路40に沿って上昇する(点線矢印参照/溶液移動工程)。結果、センサ50と改質材溶液等Yの接触部分で、改質材溶液等Yとセンサ50が相対移動する。制御装置70の測定処理部740が、バッファ空間40B内で改質材溶液等Yの移動を伴いつつ、複数回に亘って改質材溶液等YのpHを測定することで、図6(B)のように、特定深度(-16.0m)における複数のpH値が検知される。測定処理部740は、この複数pH値に基づいて、その特定深度の最終的なpH値を決定する。なお、最終的なpH値の決定方法は、これらの複数の全てのpH値の平均値を採用しても良いが、他にも、複数のpH値からノイズ成分(例えば最大値側及び最小値側のデータ又はデータ群)を除去した残データを利用して、平均値等を算出しても良く、その他の手法も採用できる。いずれにしろ、深度-16.0mの改質材溶液等Yを吸引して移動させながら、その改質材溶液等YのpH値を複数回測定することで、測定誤差を低減させる。 In the post-measurement step S126, as shown in FIG. 6A, when the pH value is measured at a specific depth (for example, a depth of -16.0 m), the depth information storage unit 730 of the control device 70 judges whether the insertion member 20 is located at the correct depth (-16.0 m) based on a signal from the drilling device 10. If necessary, the drilling device 10 may be controlled to position the insertion member 20 at the correct depth. After that, the solution movement processing unit 720 in the control device 70 controls the pressure control device 43, which serves as the solution movement means, to exhaust the gas in the solution tank 42. As a result, the modifier solution Y having a water pressure corresponding to a depth of -16.0 mm flows into the buffer space 40B through the intake port 40A and rises along the solution movement path 40 (see dotted arrow/solution movement step). As a result, the modifier solution Y and the sensor 50 move relative to each other at the contact portion between the sensor 50 and the modifier solution Y. The measurement processing unit 740 of the control device 70 measures the pH of the modifier solution Y multiple times while moving the modifier solution Y in the buffer space 40B, and multiple pH values at a specific depth (-16.0 m) are detected as shown in FIG. 6B. The measurement processing unit 740 determines the final pH value at the specific depth based on the multiple pH values. The final pH value may be determined by using the average value of all of the multiple pH values, but other methods may also be used to calculate the average value, etc., using the remaining data obtained by removing noise components (e.g., data or data groups on the maximum and minimum sides) from the multiple pH values. In any case, the measurement error is reduced by measuring the pH value of the modifier solution Y multiple times while sucking and moving the modifier solution Y at a depth of -16.0 m.

以上の工程を経て、例えば、図7の黒丸に示されるように、複数の深度(ここでは2.0m毎の深度)において、改質材溶液等YのpH値が測定される。改質材がセメントミルクの場合、改質材溶液等Yはアルカリ傾向となり、改質前溶液Zと比較してpH値が上昇する。 Through the above steps, for example, as shown by the black circles in Figure 7, the pH value of the modifier solution Y is measured at multiple depths (here, at depths of 2.0 m each). If the modifier is cement milk, the modifier solution Y tends to be alkaline, and the pH value increases compared to the pre-modification solution Z.

最後に、制御装置70における比較処理部750が、図7における改質前溶液ZのpH値(白丸)と、改質材溶液等YのpH値(黒丸)を比較して、その差分値が、所望の閾値を超えていれば、適切に改質されたと判定する(比較工程S128)。一方で、その差分値が、所望の閾値を下回れば、改質が不十分であると判定する。 Finally, the comparison processing unit 750 in the control device 70 compares the pH value (white circle) of the pre-reformed solution Z in FIG. 7 with the pH value (black circle) of the modifier solution Y, etc., and if the difference value exceeds the desired threshold, it is determined that the modification has been performed appropriately (comparison step S128). On the other hand, if the difference value is below the desired threshold, it is determined that the modification has been insufficient.

以上の通り、本実施形態の土壌改質状態測定装置1及び上記土壌改質状態測定方法によれば、測定専用に掘削される縦穴5を利用し、その縦穴5内に、改質剤そのもの、又は、改質材の少なくとも一部が溶けて生成される改質材溶液等Yを貯留し、その物性値を測定するので、土壌の改質状態を高い精度で測定することが可能となる。また、縦穴5内の改質剤そのもの、又は、改質剤が溶け出すための溶媒が不足する場合は、溶媒供給工程によって、地上から溶媒を供給するので、確実に、改質材溶液を生成することが可能となる。 As described above, the soil reformed state measuring device 1 and the soil reformed state measuring method of this embodiment utilize a vertical hole 5 excavated specifically for measurement, and store the modifier itself or a modifier solution Y generated by dissolving at least a portion of the modifier in the vertical hole 5, and measure its physical properties, making it possible to measure the reformed state of the soil with high accuracy. Also, if there is a shortage of the modifier itself in the vertical hole 5 or a solvent for dissolving the modifier, a solvent supply process supplies solvent from the ground, making it possible to reliably generate the modifier solution.

また、本実施形態では、改質材溶液等Yを測定する際に、改質材溶液等Yを溶液移動路40に沿って移動させる。このように、センサ50表面において移動を伴う改質材溶液等YのpH値を複数回に亘って測定することで、限定範囲の改質材溶液等Yではなく、広範囲の改質材溶液等Yを測定できるので、測定誤差を抑制できる。なお、本実施形態では、改質材溶液等Yを移動中にpH値を測定する場合を例示したが、測定タイミングでは改質材溶液等Yの移動(流れ)を停止し、その後、改質材溶液等Yの移動を再開し、次の測定タイミングで改質材溶液等Yの移動(流れ)を再停止させる手順を繰り返すようにしても良い。なお、この吸引した改質材溶液等Yは、地上に排出されるので、深度方向にセンサ50を移動させながら複数個所で測定する際に、深度方向における改質材溶液等Yの混合も抑制できるので、測定精度を高めることが出来る。 In addition, in this embodiment, when the modifier solution Y is measured, the modifier solution Y is moved along the solution movement path 40. In this way, by measuring the pH value of the modifier solution Y that moves on the surface of the sensor 50 multiple times, it is possible to measure a wide range of the modifier solution Y rather than a limited range of the modifier solution Y, thereby suppressing measurement errors. In this embodiment, the pH value is measured while the modifier solution Y is moving, but the movement (flow) of the modifier solution Y may be stopped at the measurement timing, and then the movement of the modifier solution Y is resumed, and the movement (flow) of the modifier solution Y is stopped again at the next measurement timing. In addition, since the aspirated modifier solution Y is discharged to the ground, when measuring at multiple points while moving the sensor 50 in the depth direction, mixing of the modifier solution Y in the depth direction can also be suppressed, thereby improving measurement accuracy.

更に本実施形態では、フィルタ44に改質材溶液等Yを通過させてから、センサ50で測定しているので、土粒がセンサ50の測定面(測定膜)に衝突して破損することを抑止できる。また、土粒によるpH値の測定誤差も抑制できる。また、溶液移動路40に進入する土粒量も抑制できるので、溶液移動路40の詰まりも抑制できる。 Furthermore, in this embodiment, since the modifier solution Y is passed through the filter 44 before being measured by the sensor 50, it is possible to prevent soil particles from colliding with and damaging the measurement surface (measurement membrane) of the sensor 50. It is also possible to reduce errors in the measurement of the pH value caused by soil particles. In addition, since the amount of soil particles entering the solution movement path 40 can be reduced, clogging of the solution movement path 40 can also be reduced.

また、本実施形態では、挿入部材20において、センサ収容部22と撮像装置収容部60が分離自在(着脱自在)となっているので、撮像装置65側を省略することもできる。一方で、両者を同時に使用する際は、撮像装置収容部60が下方側に配置されるので、センサ50による測定範囲よりも広い範囲に亘って、縦穴5の内壁を撮像できる。結果、センサ50の測定値の異常の原因を、映像の目視によって確実に分析できる。 In addition, in this embodiment, the sensor housing 22 and the imaging device housing 60 are freely separable (removable) in the insertion member 20, so the imaging device 65 can be omitted. On the other hand, when both are used simultaneously, the imaging device housing 60 is positioned on the lower side, so that the inner wall of the vertical hole 5 can be imaged over a wider range than the measurement range of the sensor 50. As a result, the cause of an abnormality in the measurement value of the sensor 50 can be reliably analyzed by visually inspecting the image.

なお、上記実施形態では、溶液移動路40によって、改質材溶液等Yを地上に排出する場合を例示したが、本発明はこれに限定されない。例えば図8に示す変形例となる挿入部材20のように、筐体に溶液放出孔40Eを形成しておき、溶液移動路40の他端を溶液放出孔40Eに連通させることができる。なお、溶液移動路40の途中には、溶液移動手段となる軸流ポンプやダイヤフラムポンプ、ブラダーポンプ等の送液手段300を配置する。このようにすると、吸入口40Aを介してバッファ空間40Bに流れ込んだ改質材溶液等Yを、溶液放出孔40Eから縦穴5内に再放出できる。このような循環経路で改質材溶液等Yを移動させながら、センサ50によるpH値を複数回測定してもよい。 In the above embodiment, the case where the modifier solution Y is discharged to the ground through the solution movement path 40 is illustrated, but the present invention is not limited to this. For example, as shown in FIG. 8, as a modified insertion member 20, a solution discharge hole 40E can be formed in the housing, and the other end of the solution movement path 40 can be connected to the solution discharge hole 40E. In addition, a liquid delivery means 300 such as an axial flow pump, a diaphragm pump, or a bladder pump, which serves as a solution moving means, is placed in the middle of the solution movement path 40. In this way, the modifier solution Y that flows into the buffer space 40B through the suction port 40A can be re-discharged from the solution discharge hole 40E into the vertical hole 5. The pH value may be measured multiple times by the sensor 50 while moving the modifier solution Y through such a circulation path.

更に本実施形態では、挿入部材20の内部に設けられる溶液移動路40にセンサ50及び温度検知部58を配置する場合を例示したが、本発明はこれに限定されない。例えば図9に示す変形例となる挿入部材20のように、筐体の外周面に検知面が露出される状態で、センサ50及び温度検知部58を配置しても良い。このようにすると、縦穴5内の改質材溶液等Yを直接測定できる。 Furthermore, in this embodiment, the sensor 50 and the temperature detection unit 58 are arranged in the solution movement path 40 provided inside the insertion member 20, but the present invention is not limited to this. For example, as in the modified insertion member 20 shown in Figure 9, the sensor 50 and the temperature detection unit 58 may be arranged with the detection surface exposed on the outer circumferential surface of the housing. In this way, the modifier solution Y in the vertical hole 5 can be directly measured.

この際、図10(A)に示すように、測定ポイントとなる特定の深度において、掘削装置(挿入装置)10を利用して、挿入部材20を上下に往復移動させながら、複数回に亘って、改質材溶液等Yの物性値を測定することが好ましい。このようにすると、センサ50と改質材溶液等Yの接触部分で、改質材溶液等Yとセンサ50を相対移動させることができるので、測定誤差を低減できる。つまり、この手法の場合、掘削装置(挿入装置)10が、改質材溶液等Yとセンサ50を相対移動させる溶液移動手段を兼ねることになる。なお、挿入部材20の上下移動距離や移動速度は特に限定されない。 At this time, as shown in FIG. 10(A), it is preferable to use the drilling device (insertion device) 10 to move the insertion member 20 up and down reciprocally at a specific depth that is the measurement point, and measure the physical property values of the modifier solution Y, etc., multiple times. In this way, the modifier solution Y and the sensor 50 can be moved relative to each other at the contact point between the sensor 50 and the modifier solution Y, etc., thereby reducing measurement errors. In other words, in this method, the drilling device (insertion device) 10 also serves as a solution moving means for moving the modifier solution Y, etc., and the sensor 50 relative to each other. Note that there is no particular limit to the vertical movement distance or movement speed of the insertion member 20.

また更に、本実施形態では、挿入部材20側にセンサ50及び温度検知部58を配置する場合を例示したが、本発明はこれに限定されない。例えば図11に示す変形例となる土壌改質状態測定装置1のように、溶液移動路40における地上側の途中にバッファタンク(測定タンク)40Tを設けるようにし、このバッファタンク40Tに一時的に貯留される改質材溶液等Yの物性値を、センサ50及び温度検知部58で測定しても良い。この際、測定ポイントとなる特定深度において、改質材溶液等Yを吸い上げてバッファタンク40Tに十分に満たしてから、物性値を測定することが好ましい。なバッファタンク40Tの貯留量は小さい方が好ましく、必要な改質材溶液等Yの吸い上げ量を抑制できる。なお、バッファタンク40Tからオーバーフローした改質材溶液等Yは、溶液タンク42に回収される。 Furthermore, in this embodiment, the sensor 50 and the temperature detection unit 58 are arranged on the side of the insertion member 20, but the present invention is not limited to this. For example, as in the soil reforming state measurement device 1 of the modified example shown in FIG. 11, a buffer tank (measurement tank) 40T may be provided on the ground side of the solution movement path 40, and the physical property value of the modifier solution Y temporarily stored in this buffer tank 40T may be measured by the sensor 50 and the temperature detection unit 58. At this time, it is preferable to measure the physical property value after sucking up the modifier solution Y at a specific depth that is the measurement point and filling the buffer tank 40T sufficiently. It is preferable that the storage amount of the buffer tank 40T is small, and the amount of the modifier solution Y that is required to be sucked up can be suppressed. The modifier solution Y that overflows from the buffer tank 40T is collected in the solution tank 42.

なお、本実施形態では、センサ50がpH値を測定する場合を例示したが、本発明はこれに限定されない。例えば、元来、高アルカリ性の土壌の場合、改質材が混ぜ合わされる前後でのpH値の差が小さく、測定精度が悪化しやすい。その場合は、元来の土壌に含まれていない(又は含まれている量が少ない)検知用電解質を改質材に含有させておき、センサ50は、この検知用電解質のみを検知できるイオン濃度計とすることが好ましい。このようにすると、土壌改質の前後において、測定されるイオン濃度の差異が大きくなるので、測定精度が向上する。 In this embodiment, the sensor 50 measures the pH value, but the present invention is not limited to this. For example, in the case of soil that is originally highly alkaline, the difference in pH value before and after the amendment is mixed in is small, and the measurement accuracy is likely to deteriorate. In that case, it is preferable to include a detection electrolyte that is not contained in the original soil (or is contained in a small amount) in the amendment, and to use the sensor 50 as an ion concentration meter that can detect only this detection electrolyte. In this way, the difference in the measured ion concentration before and after soil amendment becomes large, improving the measurement accuracy.

また、本実施形態では、溶媒として水(地下水)を用いる場合を例示したが、本発明はこれに限定されず、検出対象となる電解質が溶けやすい水以外の溶媒を用いることもできる。改質剤が高粘度流体の場合は、その粘性を低下させる溶媒を選定してもよい。 In addition, in this embodiment, the case where water (groundwater) is used as the solvent is exemplified, but the present invention is not limited to this, and a solvent other than water in which the electrolyte to be detected is easily soluble can also be used. If the modifier is a high-viscosity fluid, a solvent that reduces the viscosity may be selected.

さらに、本実施形態では、深度を減少させながら(挿入部材を上昇させながら)、複数の深度で改質材溶液等Yの物性値を測定する場合を例示したが、本発明はこれに限定されず、深度を増大させながら(挿入部材を下降させながら)測定してもよい。この際は、挿入部材で縦穴の掘削を進めつつ、各々の測定深度に達した段階で、測定を進めていくことが可能となるので、改質材又は改質剤溶液の深度方向のコンタミネーションを抑制できるという利点がある。 In addition, in this embodiment, the physical properties of the modifier solution Y are measured at multiple depths while decreasing the depth (while raising the insertion member), but the present invention is not limited to this, and measurements may be performed while increasing the depth (while lowering the insertion member). In this case, it is possible to continue the measurement when each measurement depth is reached while continuing to excavate the vertical hole with the insertion member, which has the advantage of suppressing contamination of the modifier or modifier solution in the depth direction.

尚、本発明は、上記した実施の形態に限定されるものではなく、本発明の要旨を逸脱しない範囲内において種々変更を加え得ることは勿論である。 The present invention is not limited to the above-described embodiment, and various modifications can be made without departing from the spirit of the present invention.

1 土壌改質状態測定装置
5 縦穴
10 掘削装置
12 挿入ロッド
20 挿入部材
22 センサ収容部
24 センサ側筐体
30 溶媒供給路
30A 吐出口
32 溶媒タンク
33 送液ポンプ
40 溶液移動路
40A 吸入口
40B バッファ空間
40E 溶液放出孔
40T バッファタンク
42 溶液タンク
43 圧力制御装置
44 フィルタ
50 センサ
51 感応電極
52 比較電極
58 温度検知部
60 撮像装置収容部
64 撮像装置側筐体
65 撮像装置
65A 撮像口
69 先端コーン
70 制御装置
71 コントローラ
72 検知配線
74 映像配線
76 位置情報配線
80 パーソナルコンピュータ
Y 改質材溶液等
Z 改質前溶液
1 Soil reformation state measuring device 5 Vertical hole 10 Excavation device 12 Insertion rod 20 Insertion member 22 Sensor storage section 24 Sensor side housing 30 Solvent supply path 30A Discharge port 32 Solvent tank 33 Liquid delivery pump 40 Solution movement path 40A Intake port 40B Buffer space 40E Solution discharge hole 40T Buffer tank 42 Solution tank 43 Pressure control device 44 Filter 50 Sensor 51 Sensitive electrode 52 Reference electrode 58 Temperature detection section 60 Imaging device storage section 64 Imaging device side housing 65 Imaging device 65A Imaging port 69 Tip cone 70 Control device 71 Controller 72 Detection wiring 74 Video wiring 76 Position information wiring 80 Personal computer Y Modifier solution, etc. Z Pre-modified solution

Claims (10)

地盤中に導入される土壌の改質材の拡散状態を測定する土壌改質状態測定方法であって、
前記改質材が土壌と混在していると推測される場所に形成される縦穴の内部に溜まる改質材、又は前記縦穴の内部に溜まる溶媒に前記改質材が溶けることで生成される改質材溶液を移動させる溶液移動工程と、
前記溶液移動工程によって移動される前記改質材又は前記改質材溶液の物性値を測定する溶液測定工程を備えることを特徴とする、
土壌改質状態測定方法。
A soil reforming state measurement method for measuring the diffusion state of a soil reformer introduced into the ground, comprising:
a solution transfer process for transferring the modifier accumulated in a vertical hole formed in a place where the modifier is assumed to be mixed with soil, or a modifier solution generated by dissolving the modifier in a solvent accumulated in the vertical hole;
The method further comprises a solution measurement step of measuring physical properties of the modifier or the modifier solution moved by the solution moving step.
Method for measuring soil amendment status.
前記溶液移動工程では、移動される前記改質材又は前記改質材溶液をフィルタに通過させるようにし、
前記溶液測定工程では、前記フィルタを通過した前記改質材又は前記改質材溶液の前記物性値を測定することを特徴とする、
請求項1に記載の土壌改質状態測定方法。
In the solution transfer step, the modifier or the modifier solution to be transferred is passed through a filter;
In the solution measurement step, the physical property values of the modifier or the modifier solution that has passed through the filter are measured.
The method for measuring a soil reformed state according to claim 1.
前記溶液移動工程では、前記改質材又は前記改質材溶液を地上まで移動させることを特徴とする、
請求項1または2のいずれか一項に記載の土壌改質状態測定方法。
The solution moving step is characterized in that the modifier or the modifier solution is moved to the ground.
The method for measuring a soil reformed state according to claim 1 or 2.
前記溶液測定工程では、地上に移動された前記改質材又は前記改質材溶液の前記物性値を測定することを特徴とする、
請求項3に記載の土壌改質状態測定方法。
In the solution measurement step, the physical property values of the modifier or the modifier solution moved to the ground are measured.
The method for measuring a soil reformed state according to claim 3.
地盤中に導入される土壌の改質材の拡散状態を測定する土壌改質状態測定方法であって、
前記改質材が土壌と混在していると推測される場所に形成される縦穴の内部に溜まる改質材の物性値、又は前記縦穴の内部に溜まる溶媒に前記改質材が溶けることで生成される改質材溶液の物性値を測定する溶液測定工程を備え、
前記物性値を測定するセンサと前記改質材又は前記改質材溶液の接触部分において、前記改質材又は前記改質材溶液と前記センサを相対移動させることを特徴とする、
土壌改質状態測定方法。
A soil reforming state measurement method for measuring the diffusion state of a soil reformer introduced into the ground, comprising:
A solution measurement process is provided for measuring the physical properties of the modifier stored in a vertical hole formed in a place where the modifier is assumed to be mixed with soil, or the physical properties of a modifier solution generated by dissolving the modifier in a solvent stored in the vertical hole;
The method is characterized in that the modifier or the modifier solution and the sensor are moved relative to each other at a contact portion between the sensor for measuring the physical property value and the modifier or the modifier solution.
Method for measuring soil amendment status.
共通深度において、前記改質材又は前記改質材溶液と前記センサとの相対移動を介在させて前記物性値を複数回測定することを特徴とする、
請求項5に記載の土壌改質状態測定方法。
The physical property value is measured multiple times at a common depth by intervening relative movement between the modifier or the modifier solution and the sensor.
The method for measuring a soil reformed state according to claim 5.
地盤中に導入される土壌の改質材の拡散状態を測定する土壌改質状態測定方法であって、
前記改質材が土壌と混在していると推測される場所に形成される縦穴に対して、前記改質材が溶け得る溶媒を供給する溶媒供給工程と、
前記縦穴の内部に溜まる前記溶媒に前記改質材が溶けることで生成される改質材溶液の物性値を測定する溶液測定工程と、を備えることを特徴とする、
土壌改質状態測定方法。
A soil reforming state measurement method for measuring the diffusion state of a soil reformer introduced into the ground, comprising:
a solvent supplying step of supplying a solvent capable of dissolving the modifier to a vertical hole formed in a place where the modifier is presumed to be mixed with soil;
A solution measurement process for measuring physical properties of a modifier solution generated by dissolving the modifier in the solvent stored inside the vertical hole.
Method for measuring soil amendment status.
地盤中に含侵される土壌の改質材の拡散状態を測定する土壌改質状態測定装置であって、
改質材が土壌と混在していると推測される場所に形成される縦穴に挿入される挿入部材と、
前記挿入部材に配置され、前記縦穴の内部に溜まる前記改質材の物性値又は前記縦穴の内部に溜まる溶媒に前記改質材が溶けることで生成される改質材溶液の物性値を検出するセンサと、
前記挿入部材に設けられて前記改質材又は前記改質材溶液を案内する溶液移動路と、を備え、
前記センサは、前記溶液移動路に取り込まれる前記改質材又は前記改質材溶液の物性値を検出することを特徴とする、
土壌改質状態測定装置。
A soil reforming state measuring device for measuring the diffusion state of a soil reforming material impregnated into the ground,
An insertion member to be inserted into a vertical hole formed in a location where the improvement material is presumed to be mixed with soil;
a sensor disposed in the insertion member for detecting a physical property value of the modifier stored in the vertical hole or a physical property value of a modifier solution generated by dissolving the modifier in a solvent stored in the vertical hole;
a solution passage provided in the insertion member for guiding the modifier or the modifier solution;
The sensor detects a physical property value of the modifier or the modifier solution taken into the solution movement path.
Soil reformation status measuring device.
前記溶液移動路の前記改質材又は前記改質材溶液を移動させる溶液移動手段を備えることを特徴とする、
請求項に記載の土壌改質状態測定装置。
The present invention is characterized in that a solution moving means is provided for moving the modifier or the modifier solution in the solution moving path.
The soil reformation state measuring device according to claim 8 .
前記溶液移動路は、前記改質材又は前記改質材溶液を地上まで案内することを特徴とする、
請求項及びのいずれか一項に記載の土壌改質状態測定装置。
The solution transfer path is characterized in that it guides the modifier or the modifier solution to the ground.
The soil reformation state measuring device according to any one of claims 8 and 9 .
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