JP7025614B2 - Method of reforming mixed soil with bubbles - Google Patents
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- JP7025614B2 JP7025614B2 JP2018165857A JP2018165857A JP7025614B2 JP 7025614 B2 JP7025614 B2 JP 7025614B2 JP 2018165857 A JP2018165857 A JP 2018165857A JP 2018165857 A JP2018165857 A JP 2018165857A JP 7025614 B2 JP7025614 B2 JP 7025614B2
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Description
本発明は、気泡混合土砂の改質処理方法に関するものである。 The present invention relates to a method for modifying a bubble-mixed soil.
従来、シールド工事、推進工事のような建設工事等で発生する泥土、すなわち、高含水比の軟弱な土砂は、産業廃棄物として脱水処理した後、最終処分場に埋立てて廃棄処理されている。こうした泥土の処理は、脱水処理に経費がかかる上、脱水処理した泥土も、産業廃棄物として再利用することなく廃棄しなければならないため、著しく非経済的である。また、このように泥土を処理して廃棄するにしても、最近は、産業廃棄物の最終処分地の立地難が深刻化している。 Conventionally, mud that is generated in construction work such as shield work and propulsion work, that is, soft earth and sand with a high water content, is dehydrated as industrial waste and then landfilled in a final disposal site for disposal. .. The treatment of such mud is extremely uneconomical because the dehydration treatment is expensive and the dehydrated mud must be disposed of without being reused as industrial waste. Moreover, even if the mud is treated and disposed of in this way, the difficulty in locating the final disposal site for industrial waste has become more serious recently.
こうしたことを背景にして建設工事等で発生する泥土のリサイクルの必要性が高まっている。こうした要請から、これまで利用価値のなかった泥土について、施工業者自らが泥土の発生現場で改質剤を混合して改質処理を施すことにより、これを強度の高い一般建設残土と同等の土砂に改質して利用価値を創出し、改質処理現場から再利用先へと直接搬送して、路盤材、埋め戻し土、宅地造成土、土手の盛土等の種々の用途に再利用する技術の開発が進められている(例えば、特許文献1参照。)。 Against this background, there is an increasing need to recycle mud generated during construction work. In response to these demands, the contractor himself mixed a modifier and reformed the mud, which had not been used until now, at the site where the mud was generated. Technology that creates utility value by reforming the soil, transports it directly from the reforming treatment site to the reuse destination, and reuses it for various purposes such as roadbed materials, backfill soil, residential land development soil, and embankment of embankments. Is under development (see, for example, Patent Document 1).
ところで、泥土の改質処理に用いる改質剤の代表的なものとして、アニオン性高分子凝集剤を挙げることができるが、シールド工事、推進工事等で用いられる掘削添加材(界面活性剤に高分子系加泥材やカルボキシメチルセルロース(CMC)等のアニオン性増粘剤を添加した起泡材やベントナイト)が多量に含まれる掘削土等では、アニオン性高分子凝集剤のみでは十分な改質ができず、搬送が可能な自立性を有する土砂への改質が困難な場合があった。
また、掘削添加材に起泡剤としてアニオン系界面活性剤のみが使用された土砂に、アニオン性高分子凝集剤を用いて改質した土砂は、降雨等により起泡剤を構成するアニオン系界面活性剤が溶出し、泡立ちが問題となる場合があった。
By the way, an anionic polymer flocculant can be mentioned as a typical modifier used for the reforming treatment of mud, but it is a drilling additive used in shielding work, propulsion work, etc. For excavated soil containing a large amount of (foaming material or bentonite) to which an anionic thickener such as molecular mud material or carboxymethyl cellulose (CMC) is added, sufficient modification can be achieved with the anionic polymer flocculant alone. In some cases, it was not possible to reform the soil into self-sustaining earth and sand that could be transported.
Further, the earth and sand modified by using an anionic polymer flocculant on the earth and sand in which only an anionic surfactant is used as a foaming agent in the excavation additive is an anionic interface constituting the foaming agent by rainfall or the like. In some cases, the activator was eluted and foaming became a problem.
また、アニオン性高分子凝集剤のみによって改質された土砂は、降雨等により起泡剤を構成する界面活性剤の溶出により、泡立ちのあるろ水が河川や地下水に流れ込むおそれや、海上埋立地での泡立ち、中間処理場での排土の分級処理等の中間処理時の泡の発生に伴う歩掛の低下等の二次的問題を引き起こすおそれがあった。 In addition, the earth and sand modified only by the anionic polymer flocculant may cause foaming filter water to flow into rivers and groundwater due to the elution of the surfactant that constitutes the foaming agent due to rainfall, etc., and the landfill site at sea. There was a risk of causing secondary problems such as foaming in the water and a decrease in yield due to the generation of foam during intermediate treatment such as classification treatment of soil waste in the intermediate treatment plant.
このような場合、アニオン性高分子凝集剤に代えて、カチオン価の高い、カチオン性高分子凝集剤を用いることによって改質を行うことができることが知られている(例えば、特許文献2参照。)が、カチオン価が高く、分子量の大きいカチオン性高分子凝集剤は、魚毒性が高く、改質後の土砂を再利用する場合にカチオン性高分子凝集剤が溶出することが問題視されていた。 In such a case, it is known that the modification can be performed by using a cationic polymer flocculant having a high cationic value instead of the anionic polymer flocculant (see, for example, Patent Document 2). ) However, the cationic polymer flocculant having a high cationic value and a large molecular weight is highly toxic to fish, and it is regarded as a problem that the cationic polymer flocculant elutes when the reformed earth and sand are reused. rice field.
本発明は、上記のアニオン性高分子凝集剤の単独添加による自立性を有する土砂への改質が困難な泥土等の流動性を有する土砂、特に、気泡混合土砂の改質処理方法に伴う問題点に鑑み、アニオン性増粘剤やベントナイト等を含有する気泡混合土砂を、高分子凝集剤の単独添加することによって自立性を有する土砂への改質処理するに当たり、起泡剤を構成するアニオン性界面活性剤の溶出に伴う二次的問題やカチオン性高分子凝集剤の使用による魚毒性の問題を解消できる気泡混合土砂の改質処理方法を提供することを目的とする。 INDUSTRIAL APPLICABILITY The present invention has a problem associated with a method for modifying a fluid-like sediment such as mud, which is difficult to reform into a self-sustaining sediment by adding the above-mentioned anionic polymer flocculant alone, particularly a bubble-mixed sediment. In view of this point, the anion constituting the foaming agent is used to modify the foam-mixed earth and sand containing an anionic thickener, bentonite, etc. into the earth and sand having self-sustaining property by adding the polymer flocculant alone. It is an object of the present invention to provide a method for modifying a bubble-mixed earth and sand that can solve the secondary problem associated with the elution of a sex surfactant and the problem of fish toxicity due to the use of a cationic polymer flocculant.
上記目的を達成するため、本発明の気泡混合土砂の改質処理方法は、気泡混合土砂の改質処理方法において、前記気泡混合土砂に、両性高分子凝集剤を添加撹拌し、イオンコンプレックスによって水不溶性物質を生成させることで、気泡混合土砂を自立性を有する土砂に改質することを特徴とする。 In order to achieve the above object, the method for modifying the bubble-mixed soil of the present invention is the method for modifying the bubble-mixed soil, in which an amphoteric polymer flocculant is added to the bubble-mixed soil and stirred, and water is added to the ion complex. It is characterized by reforming a bubble-mixed earth and sand into a self-sustaining earth and sand by generating an insoluble substance.
この場合において、前記両性高分子凝集剤には、pH6~8の中性域においてカチオンモル数がアニオンモル数を下回る重合比の両性高分子凝集剤を用いることができる。 In this case, as the amphoteric polymer flocculant, an amphoteric polymer flocculant having a polymerization ratio in which the number of cation moles is lower than the number of anion moles in the neutral range of pH 6 to 8 can be used.
また、前記気泡混合土砂は、アニオン性界面活性剤を含有するものであったり、アニオン性増粘剤及び/又はベントナイトを含有するものを対象とすることができる。 Further, the bubble-mixed earth and sand may be one containing an anionic surfactant, or one containing an anionic thickener and / or bentonite.
本発明の気泡混合土砂の改質処理方法によれば、気泡混合土砂に、両性高分子凝集剤を添加撹拌し、イオンコンプレックスによって水不溶性物質を生成させることで、アニオン性界面活性剤又はアニオン性増粘剤やベントナイト等を含有する気泡混合土砂を自立性を有する土砂に改質することができ、併せて、イオンコンプレックスによる水不溶化により、カチオン成分の溶出を抑制し、魚毒性の問題や起泡剤を構成する界面活性剤の溶出に伴う二次的問題を解消することができる。 According to the method for modifying the bubble-mixed sediment of the present invention, an amphoteric polymer flocculant is added to the foam-mixed sediment and stirred to generate a water-insoluble substance by an ion complex, whereby an anionic surfactant or anionic surfactant or anionic. Bubble-mixed sediment containing thickeners, bentonite, etc. can be reformed into self-sustaining sediment, and at the same time, water insolubilization by an ion complex suppresses elution of cation components, causing problems of fish toxicity and problems. It is possible to solve the secondary problem associated with the elution of the surfactant constituting the foaming agent.
以下、本発明の気泡混合土砂の改質処理方法の実施の形態を、具体的な実施形態に基づいて説明する。 Hereinafter, embodiments of the method for modifying bubble-mixed soil of the present invention will be described based on specific embodiments.
本発明の気泡混合土砂の改質処理方法は、気泡混合土砂に、両性高分子凝集剤を添加撹拌し、イオンコンプレックスによって水不溶性物質を生成させることで、アニオン性界面活性剤又はアニオン性増粘剤やベントナイト等を含有する気泡混合土砂を自立性を有する土砂に改質することができ、併せて、水不溶化により、カチオン成分の溶出を抑制し、起泡剤を構成するアニオン性界面活性剤の溶出に伴う二次的問題やカチオン性高分子凝集剤の使用による魚毒性の問題を解消するようにしたものである。 In the method for modifying the bubble-mixed sediment of the present invention, an amphoteric polymer flocculant is added to the foam-mixed sediment and stirred to generate a water-insoluble substance by an ion complex, whereby an anionic surfactant or an anionic thickening agent is produced. A bubble-mixed earth and sand containing agents, bentonite, etc. can be modified into self-sustaining earth and sand, and at the same time, anionic surfactant that suppresses elution of cationic components by water insolubilization and constitutes a foaming agent. It is intended to solve the secondary problem associated with the elution of foam and the problem of fish toxicity due to the use of a cationic polymer flocculant.
ここで、「自立性を有する土砂」とは、ダンプトラックを使用して土砂を改質処理現場から再利用先へと直接搬送することが可能な程度の土砂を意味し、より具体的には、ミニスランプ試験によるスランプ値が1.0cm以下の土砂を意味する。 Here, "self-sustaining soil" means soil that can be directly transported from the reforming treatment site to the reuse destination using a dump truck, and more specifically. , Means earth and sand with a slump value of 1.0 cm or less as determined by the mini slump test.
ところで、気泡混合土砂に、両性高分子凝集剤を添加、撹拌した場合、概ねpHが中性域(pH6~8)ではカチオン部とアニオン部のどちらもイオン解離し、カチオンは界面活性剤のアニオン電荷や増粘剤などのアニオン電荷とイオン結合し、場合によっては自身のアニオン部とイオン結合してイオンコンプレックスを作りながら水不溶性物質となる。
このとき、水不溶解性物質中に起泡剤を構成するアニオン性界面活性剤やアニオン性増粘剤が水不溶性物質となることによって、気泡を構成する界面活性剤の溶出に伴う二次的問題を解消することができる。
By the way, when an amphoteric polymer flocculant is added to the bubble-mixed earth and sand and stirred, both the cation part and the anion part are ionically dissociated in the neutral pH range (pH 6 to 8), and the cation is the anion of the surfactant. It becomes a water-insoluble substance while forming an ionic complex by ionic bonding with an anionic charge such as an electric charge or a thickener and, in some cases, ionic bonding with its own anionic part.
At this time, the anionic surfactant and the anionic thickener constituting the foaming agent in the water-insoluble substance become water-insoluble substances, so that the secondary surfactant associated with the elution of the surfactant constituting the bubbles becomes secondary. The problem can be solved.
この場合、両性高分子凝集剤は、重合させるアニオン性材料やカチオン性材料に限定はなく、pH6~8の中性域においてカチオンモル数がアニオンモル数を下回る重合比であれば、より確実に、カチオン成分の溶出を抑制し、魚毒性の問題を解消することができる。この両性高分子凝集剤としては、より具体的には、分子量500万~2500万の範囲において、アニオン部が20モル%~40モル%カチオン部が0.1モル%~20モル%の範囲において選択的に用いることが可能であり、アニオン部とカチオン部の対比においては用いられる掘削添加剤のアニオン価に応じて、カチオン価を増減(掘削添加剤のアニオン価が高い場合はカチオン価を高めに、低い場合はカチオン価を低めに)することができる。 In this case, the amphoteric polymer flocculant is not limited to the anionic material or the cationic material to be polymerized, and if the polymerization ratio is such that the number of cation moles is less than the number of anion moles in the neutral range of pH 6 to 8, the cation is more reliably used. It is possible to suppress the elution of components and solve the problem of fish toxicity. More specifically, the amphoteric polymer flocculant has a molecular weight of 5 million to 25 million, an anion portion of 20 mol% to 40 mol%, and a cation portion of 0.1 mol% to 20 mol%. It can be used selectively, and in the comparison between the anion part and the cation part, the cation value is increased or decreased according to the anion value of the excavation additive used (if the anion value of the excavation additive is high, the cation value is increased). If it is low, the cation value can be lowered).
以下、以下の条件で、アニオン性高分子凝集剤と両性高分子凝集剤をそれぞれ用いて気泡混合土砂の改質処理の比較試験を行った結果を、表1及び表2に示す。 Below, Tables 1 and 2 show the results of comparative tests of the modification treatment of the bubble-mixed soil using the anionic polymer flocculant and the amphoteric polymer flocculant under the following conditions.
アニオン性増粘剤(カルボキシメチルセルロース塩)入り起泡剤(ラウリルエーテル硫酸塩)1%水溶液
乾燥川砂
加水15%(耐乾燥川砂1Lに150ml)
気泡注入20%(加水川砂1Lに300mlの気泡を注入)
Foaming agent (lauryl ether sulfate) containing anionic thickener (carboxymethyl cellulose salt) 1% aqueous solution Dry river sand 15% water (150 ml in 1 L of dry river sand)
Bubble injection 20% (Inject 300 ml of bubbles into 1 L of water river sand)
起泡剤(ラウリルエーテル硫酸塩)1%水溶液
乾燥川砂
加水15%(耐乾燥川砂1Lに150ml)
気泡注入30%(加水川砂1Lに300mlの気泡を注入)
Foaming agent (lauryl ether sulfate) 1% aqueous solution Dry river sand 15% water (150 ml in 1 L of dry river sand)
Bubble injection 30% (Inject 300 ml of bubbles into 1 L of water river sand)
上記の比較試験の結果から、両性高分子凝集剤は、アニオン性高分子凝集剤と比較して、気泡混合土砂の改質処理において良好な改質性を発揮することを確認した。 From the results of the above comparative test, it was confirmed that the amphoteric polymer flocculant exhibits better reformability in the reforming treatment of the bubble-mixed soil as compared with the anionic polymer flocculant.
以上、本発明の気泡混合土砂の改質処理方法について、その実施形態に基づいて説明したが、本発明は上記実施形態に限定されるものではなく、その趣旨を逸脱しない範囲において適宜その構成を変更することができるものである。 The method for modifying the bubble-mixed soil of the present invention has been described above based on the embodiment, but the present invention is not limited to the above embodiment, and the configuration thereof is appropriately configured as long as the purpose is not deviated. It can be changed.
本発明の気泡混合土砂の改質処理方法は、アニオン性界面活性剤又はアニオン性増粘剤やベントナイト等を含有する気泡混合土砂を、高分子凝集剤の単独添加することによって自立性を有する土砂への改質処理するに当たり、起泡剤を構成するアニオン性界面活性剤の溶出に伴う二次的問題やカチオン性高分子凝集剤の使用による魚毒性の問題を解消できることから、アニオン性高分子凝集剤の単独添加による自立性を有する土砂への改質が困難な泥土等の流動性を有する土砂、特に、気泡混合土砂の改質処理の用途に好適に用いることができる。 In the method for modifying a bubble-mixed earth and sand of the present invention, a cell-mixed earth and sand containing an anionic surfactant, an anionic thickener, bentonite and the like is added alone as a polymer flocculant to have self-sustaining earth and sand. Since it is possible to solve the secondary problem associated with the elution of the anionic surfactant constituting the foaming agent and the problem of fish toxicity due to the use of the cationic polymer flocculant, the anionic polymer can be modified. It can be suitably used for reforming earth and sand having fluidity such as mud soil which is difficult to be modified into self-sustaining earth and sand by adding a flocculant alone, particularly foam-mixed earth and sand.
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| JPS6066792U (en) * | 1983-10-17 | 1985-05-11 | 石川島播磨重工業株式会社 | shield tunneling machine |
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| JP3034684B2 (en) | 1992-02-12 | 2000-04-17 | クラレケミカル株式会社 | Slurry material for propulsion method |
| JP2000325966A (en) | 1999-05-24 | 2000-11-28 | Toagosei Co Ltd | Dehydration treatment method of muddy water |
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