JP2005336232A - Soil solidification agent - Google Patents

Soil solidification agent Download PDF

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JP2005336232A
JP2005336232A JP2004153324A JP2004153324A JP2005336232A JP 2005336232 A JP2005336232 A JP 2005336232A JP 2004153324 A JP2004153324 A JP 2004153324A JP 2004153324 A JP2004153324 A JP 2004153324A JP 2005336232 A JP2005336232 A JP 2005336232A
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agent
soil
solidification
blast furnace
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Hiromi Nakajima
博己 中嶋
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SHOKUDAI HANBAI KK
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SHOKUDAI HANBAI KK
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

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  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)
  • Curing Cements, Concrete, And Artificial Stone (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To obtain a soil solidification agent which is effective for the solidification of organic/inorganic soft soils produced by dredging or at construction sites, confines heavy metals or malodors in the solidified soil, does not re-elute them, prevents secondary environmental contamination, is applicable for a spray seeding work which is water resistant and not washed away by rain and improves soils for reutilization. <P>SOLUTION: This soil solidification agent comprises 60-90 wt.% of [agent A] a base component of the solidification agent which is a homogeneous mixture of 60-90 wt.% of paper making sludge ash or flyash and 10-30 wt.% of blast furnace cement or Portland cement and 10-40 wt.% of [agent B] as a reactive agent of the solidification agent which is a mixture of 10-20 wt.% of aluminum sulfate, 20-30 wt.% of blast furnace slag, 40-60 wt.% of calcium sulfate, 10-20 wt.% of silicon dioxide (silica), 10-20 wt.% of sodium carbonate and 10-20 wt.% of sodium sulfate. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は浚渫・建設現場から発生する有機・無機性の軟弱土壌の固化処理に有効であり、重金属類や悪臭を固体生成物に封じ込め、再溶出させず二次的環境汚染を防止し、土壌を改良して再利用を可能にする土壌固化処理剤に関する。   The present invention is effective for solidifying organic / inorganic soft soil generated from dredging / construction sites, containing heavy metals and odors in solid products, preventing secondary environmental pollution without re-elution, It is related with the soil solidification processing agent which improves and enables reuse.

従来、河川・湖沼からの浚渫土あるいは建設現場等から発生する軟弱土壌の固化にはセメント系固化剤や石灰系固化剤等が多く使用されている。石灰系固化剤はヘドロや有機質土壌に対して限定的に使用されている。しかし、これら固化剤を使用した場合にpHが強アルカリ性となり自然環境の生態系に悪影響をおよぼす結果となり、また、セメント系固化剤はその固化の機構から、対象土壌に有機物があると固化反応が阻害されたり、ときには全く効果を示さないことがある。一方、石灰系固化剤は適用範囲は広いが、固化土壌から長期にわたりアルカリ成分が浸出するという問題が残る。セメント系固化剤はでは固化に要する養生期間が4〜7日程度かかり軟弱土と混合してからすぐに搬出または作業ができない等の欠点があり、浚渫汚泥が混在していると、セメントの水和硬化反応が阻害され、固化剤としての機能を失うことがある。また、六価クロムが溶出する場合もあり問題がある。一方、石灰系固化剤では高熱を発し水蒸気が出て悪臭が発生する等の問題があるほか、固化処理後の処理物からアルカリが溶出するという問題があり、環境保全の点からみても大きな問題を抱えている。また、これら固化剤では固化強度の調整ができず掘り返しができないため再利用が不可能であり、掘り起こした場合は産業廃棄物処理をしなければならないという問題がある。従来の固化剤は、軟弱土壌等に溶存している重金属や悪臭源等を固定することができないため、固化処理後の処理物からこれらの有害物質が溶出しやすいということが言える。   Conventionally, cement-based solidifying agents, lime-based solidifying agents and the like are often used for solidifying soft soil generated from dredged soil from rivers and lakes or construction sites. Lime-based solidifying agents are limited to sludge and organic soils. However, when these solidifying agents are used, the pH becomes strongly alkaline and adversely affects the ecosystem of the natural environment. Also, cement solidifying agents have a solidification reaction due to the solidification mechanism, and if there is organic matter in the target soil. It may be hindered or sometimes not effective at all. On the other hand, the application range of the lime-based solidifying agent is wide, but the problem that the alkaline component leaches out from the solidified soil for a long time remains. Cement-based solidifying agents have a drawback that the curing period required for solidification is about 4 to 7 days, and they cannot be carried out or worked immediately after mixing with soft soil. The Japanese curing reaction is inhibited, and the function as a solidifying agent may be lost. There is also a problem that hexavalent chromium may be eluted. On the other hand, the lime-based solidifying agent has problems such as high heat, water vapor and bad odor, etc., and there is a problem that alkali is eluted from the treated product after solidification treatment, which is a big problem from the viewpoint of environmental conservation. Have Further, these solidifying agents cannot adjust the solidification strength and cannot be dug up, so that they cannot be reused, and when they are dug up, there is a problem that industrial waste must be treated. Since conventional solidifying agents cannot fix heavy metals dissolved in soft soil or the like, odor sources, etc., it can be said that these harmful substances are likely to be eluted from the treated product after the solidification treatment.

ほかに、本発明が意図するものに類似するものとして特許文献1がみられ、製紙スラッジ灰を原料として50〜70重量%、高炉スラグ10重量%と、石灰もしくは生石灰を10〜20重量%、硫酸カルシウム10〜20重量%と混合した土壌固化剤を用いているが、重機で作業可能な状態になるまで2時間を要し、連続的な作業ができないので、連続的な作業が必要な現場には向かない。
特開2002-88362
In addition, Patent Document 1 is seen as being similar to the one intended by the present invention. Paper sludge ash is used as a raw material, 50 to 70% by weight, blast furnace slag 10% by weight, lime or quick lime 10 to 20% by weight, A soil solidifying agent mixed with 10 to 20% by weight of calcium sulfate is used, but it takes 2 hours to be able to work with heavy machinery, and continuous work is not possible. Not suitable for.
JP2002-88362

本発明は浚渫・建設現場等から発生する有機・無機性の軟弱土壌の固化処理に有効であり、重金属類や悪臭を固化生成物に封じ込め、再溶出させず、2次環境汚染を防止し、水に強く、雨等にも流出しない緑化吹き付け用の応用も可能な、土壌を改良して再利用を可能にする土壌固化処理剤を提供せんとするものである。   The present invention is effective for solidifying organic / inorganic soft soil generated from dredging / construction sites, etc., containing heavy metals and odors in the solidified product, preventing re-elution, preventing secondary environmental pollution, It is intended to provide a soil solidification treatment agent that is resistant to water and that can be applied for greening spraying that does not flow out into the rain, etc., and that can improve soil and reuse it.

ここにおいて本発明者は土壌固化処理剤として、製紙スラッジ灰またはフライアッシュ60-90 重量%、高炉セメントまたはポルトランドセメント10-30 重量%を均一に混合した固化剤主剤[A剤]60-90 重量%と、硫酸アルミニウム10-20 重量%、高炉スラグ20-30 重量%、硫酸カルシウム40-60 重量%、二酸化珪素10-20 重量%、炭酸ナトリウム10-20 重量%、硫酸ナトリウム10-20 重量%を混合した固化剤反応剤[B剤]10-40 重量%とからなるものを見出すに至った。   Here, the present inventor, as a soil solidifying agent, solidified main agent [agent A] 60-90 wt% in which paper sludge ash or fly ash 60-90 wt% and blast furnace cement or Portland cement 10-30 wt% were uniformly mixed. %, Aluminum sulfate 10-20 wt%, blast furnace slag 20-30 wt%, calcium sulfate 40-60 wt%, silicon dioxide 10-20 wt%, sodium carbonate 10-20 wt%, sodium sulfate 10-20 wt% As a result, a solidifying agent reactant [B agent] mixed with 10 to 40% by weight was found.

本発明の土壌固化処理剤は、自身で固化することがなく、悪臭を吸収し、透水性が良く、掘り起こしが容易であり、植生が非常に良く、強い雨等にも流失することがなく、改良後も良い土壌として再利用することができる。
なお、本発明の主原料は、製紙スラッジ灰やフライアッシュであるため、従来、製紙工場や電力会社などで産業産業廃棄物処理をしていたものを再利用するということで産業廃棄物の減量化、強いては最終処分場の延命にも貢献する。
The soil solidification treatment agent of the present invention does not solidify itself, absorbs bad odors, has good water permeability, is easy to dig up, has very good vegetation, and does not run away even in strong rain, Even after improvement, it can be reused as good soil.
Since the main raw material of the present invention is paper sludge ash and fly ash, the amount of industrial waste can be reduced by reusing what was conventionally treated as industrial industrial waste at paper mills and power companies. In other words, it contributes to extending the life of the final disposal site.

本発明の土壌固化処理剤は、アルカリを溶出せず、植生にも影響を与えず、周辺環境にも影響を与えない。また、セメント系・石灰系に比しても投入量が3〜7%と少なく、攪拌終了後すぐに重機での作業が可能となる。また、本発明の土壌安定剤はポーラスな構造内部に多量の水分を結晶水として固定し、同時に有害成分の吸収固化を促進し、さらに有害重金属を封じ込むとともに消臭効果も発揮する。   The soil solidifying agent of the present invention does not elute alkali, does not affect vegetation, and does not affect the surrounding environment. In addition, the input amount is as small as 3 to 7% as compared with cement-based and lime-based materials, and it becomes possible to work with heavy machinery immediately after the completion of stirring. In addition, the soil stabilizer of the present invention fixes a large amount of water as crystal water inside the porous structure, and at the same time, promotes absorption and solidification of harmful components, further encloses harmful heavy metals and exerts a deodorizing effect.

本発明の土壌固化処理剤は、前記焼却灰を主成分とし、硫酸アルミニウム・硫酸カルシウム・硫酸ナトリウム・二酸化珪素・炭酸ナトリウム・高炉スラグを各々配合したもので、共存する水との間で水和反応が確実に進み、エトリンガイトを生成して優れた吸水作用が発揮される。これにより、多量の水分を水和反応自体で消費するとともに、その反応により生成される水和物中に多量の有機物・有害重金属などを取り込む。   The soil solidification treatment agent of the present invention is mainly composed of the incinerated ash, and contains aluminum sulfate, calcium sulfate, sodium sulfate, silicon dioxide, sodium carbonate, and blast furnace slag, and is hydrated with coexisting water. The reaction proceeds with certainty, producing ettringite and exhibiting excellent water absorption. As a result, a large amount of water is consumed by the hydration reaction itself, and a large amount of organic matter, harmful heavy metals, etc. are taken into the hydrate produced by the reaction.

さらに、本発明ではポーラスな構造に吸水することにより、ヘドロの水分に溶け込んでいる成分が原因である汚泥中の臭気を吸水固化により短時間で軽減し、固化終了段階ではほとんど臭いの無いものに変える性質がある。また、物理的吸水作用により、イオン状態で存在する重金属類などの有害物質を取り込む作用があり、さらに取り込んだ物質の再溶出を防ぐ作用もある。   Furthermore, in the present invention, by absorbing water into a porous structure, the odor in the sludge caused by the components dissolved in the sludge moisture is reduced in a short time by water absorption solidification, and there is almost no odor at the end of solidification. There is a nature to change. In addition, the physical water absorption action has an action of taking in harmful substances such as heavy metals existing in an ionic state, and further has an action to prevent re-elution of the taken-in substances.

このことから、本発明の土壌固化処理剤は、急速固化が要求される現場や有機物が多く含まれる現場などに有効である。また、対象土壌に有害物質や悪臭を放つ物質がある場合は、これらの物質の封じ込めや処理に適応する。さらに、締め固めの調整をすることにより、透水係数を保ち、改良後の適用地の緑化にも有効である。   For this reason, the soil solidification treatment agent of the present invention is effective in a site where rapid solidification is required or a site containing a large amount of organic matter. In addition, if there are harmful substances or odorous substances in the target soil, it is applicable to containment and treatment of these substances. Furthermore, by adjusting the compaction, the hydraulic conductivity is maintained, and it is effective for the greening of the application area after improvement.

本発明の土壌固化処理剤は無機・有機を含む各種の土壌、例えば、高含水率汚泥、無機・有機のシルト、腐食土の処理の改良処理に安定した機能を発揮することができ、臭気・有害物質を封じ込め、再溶出を防止することができる。しかも、固化助剤の緩衝作用で安定化処理後の土壌のpHを中性域に維持するので環境保全上きわめて有利である。また、処理土壌の透水性が保たれるので土壌改良後の緑化が求められるところに最適である。さらに、処理土壌の透水性・封じ込め・一般土壌との融合・掘り起こしが可能であるなど各特性が作用し汚泥の再利用が可能である。   The soil solidification treatment agent of the present invention can exhibit a stable function in various soils containing inorganic and organic materials, for example, high moisture content sludge, inorganic and organic silt, and improved treatment of corrosive soils. Contain toxic substances and prevent re-elution. Moreover, since the pH of the soil after the stabilization treatment is maintained in a neutral range by the buffering action of the solidification aid, it is extremely advantageous for environmental protection. Moreover, since the water permeability of the treated soil is maintained, it is optimal for a place where greening after soil improvement is required. In addition, various properties such as water permeability, containment of the treated soil, fusion with general soil, and excavation are possible, and sludge can be reused.

このように、適用範囲が広いので、処理対象土質の変化による大幅な添加量の変更もなく工程管理上きわめて有利である。なお、比重が小さく、セメント系の固化剤に比し処理後の土壌の輸送コストの面で利点があるといえる。   Thus, since the application range is wide, there is no significant change in the amount of addition due to changes in the soil to be treated, which is extremely advantageous for process management. The specific gravity is small and it can be said that there is an advantage in terms of the transportation cost of the soil after the treatment as compared with the cement-based solidifying agent.

本発明の土壌固化処理剤は製紙スラッジ灰やフライアッシュを主成分とし、アルカリ調製剤、緩衝剤、固化序剤を配合して製造したもので比重が比較的小さく、灰色の粉体である。本発明の土壌固化処理剤の特色の一つは主成分である製紙スラッジ灰やフライアッシュの物理的構造にあるといえる。製紙スラッジ灰やフライアッシュは高温燃焼による微細な無機質の生成物であるため、粒子の空隙率(ポロシティ)が高く、このことが活性炭の作用等に似た有機物・無機物に対する吸着性能を示す。したがって、汚泥中に存在する臭気・悪臭成分(硫化水素、有機物の嫌気性条件で分解生成する揮発性有機酸・低級アミン・アンモニア等)を吸着し、さらに強い吸水性とその後に続く物理化学反応で生成する水和物の作用で吸着物の再溶出を防ぐ。この作用は有機物に限ったことではなく、無機重金属類の溶存有害物質に対しても同時に進行する固化の過程で現れる物理化学的反応によって包接的に封じ込めてしまう。石灰系固化剤の場合、アルカリの溶出が続き植生に悪影響を与えると述べたが、本発明の土壌固化剤は添加助剤の作用で安定的に中性域のpHを保持するので植生の環境を良好に保つことができる。   The soil solidification treatment agent of the present invention is a gray powder having a relatively small specific gravity, which is produced by blending a papermaking sludge ash or fly ash as a main component with an alkali preparation agent, a buffering agent, and a solidifying agent. It can be said that one of the features of the soil solidifying agent of the present invention is the physical structure of papermaking sludge ash and fly ash which are the main components. Since paper sludge ash and fly ash are fine inorganic products produced by high-temperature combustion, the porosity of the particles is high, and this shows adsorption performance for organic and inorganic substances similar to the action of activated carbon. Therefore, it absorbs odors and malodorous components (hydrogen sulfide, volatile organic acids, lower amines, ammonia, etc. that are decomposed and generated under anaerobic conditions of organic matter) present in the sludge, stronger water absorption and subsequent physicochemical reaction Re-elution of adsorbate is prevented by the action of hydrate produced in This action is not limited to organic substances, but it is contained in a clathrate by physicochemical reactions that appear in the process of solidification proceeding simultaneously with dissolved harmful substances of inorganic heavy metals. In the case of the lime-based solidifying agent, it was said that alkali elution continued and adversely affected vegetation. Can be kept good.

硬化の特性について以下に述べる。[初期硬化]について述べれば、本発明の土壌固化処理剤は化学反応の一環として水を取り入れるセメント系固化剤と異なり、主成分である製紙スラッジ灰やフライアッシュの投入初期に起こる急速な物理的吸水作用と引き続き進行する化学反応が早期に初期強度を高めることに関わっている。[中期硬化]については、製紙スラッジ灰やフライアッシュの有機物吸着効果によって、有機物の溶存を嫌う凝固助剤の凝結効果が高まり中期強度の増大が図られる。[長期高度]については、土壌中のコロイド粒子を長期の固化反応過程に組み込むことにより強度の増加と周辺土壌とのなじみを時間をかけながらバランスよく実現するようにしてある。   The characteristics of curing are described below. [Initial curing] The soil solidifying agent of the present invention is different from a cement-based solidifying agent that takes in water as part of a chemical reaction. Water absorption and subsequent chemical reactions are involved in increasing the initial strength early. With regard to [Medium-term curing], the coagulation effect of the coagulation aid that dislikes the dissolution of organic substances is increased by the organic substance adsorption effect of papermaking sludge ash and fly ash, and the medium-term strength is increased. With regard to [long-term altitude], by incorporating colloidal particles in the soil into the long-term solidification reaction process, the increase in strength and the familiarity with the surrounding soil are realized in a balanced manner over time.

以下、本発明の土壌固化処理剤の施工方法についてさらに具体的に説明する。使用機械にはバックホー・スタビライザー・耕転機などがあるが、バックホーを例にとり説明する。処理対象の土壌の容積に比重(通常、1.6 )を掛け、それに対する固化剤の添加割合(投入率)として土壌の質により3〜7%で使用する。[散布]にあたり本発明の土壌固化剤を地面に置きバックホーを横向きにしてフレコン袋の底を十文字に切り飛散させずに散布するが、散布にはセメント散布機などを使用する方法もある。   Hereinafter, the construction method of the soil solidification treatment agent of the present invention will be described more specifically. The machines used include backhoes, stabilizers, and tillers. The backhoe will be described as an example. Multiply the specific volume (usually 1.6) by the volume of the soil to be treated and use it at 3-7% depending on the quality of the soil. In the [spreading], the soil solidifying agent of the present invention is placed on the ground and the backhoe is turned sideways, and the bottom of the flexible container bag is cut and scattered without crossing, but there is also a method using a cement spreader or the like.

[攪拌]にあたり、バックホーを使用する場合はバケットの裏面も使用して、極力大きな粒が無くなるように、また団子状にならないようにこまめに攪拌することがが肝心である。土の色が一様になるように攪拌することがコツである。攪拌には攪拌機を使用する方法もある。 When using a backhoe, it is important to use the back side of the bucket and stir frequently so that no large particles are lost and do not form dumplings. The trick is to stir so that the soil color is uniform. There is also a method of using a stirrer for stirring.

[転圧]にあたり、要求される締め固めにより変わるが、30cm程度ごとに転圧することが望まれる。転圧は攪拌後、バックホーのバケットの裏面で叩きつけておこなう。その後さらにバックホーで踏み付け、仕上げに振動ローラーなどを使用する。また、土面を平らにする必要があるときは、、グレーダー・ブルトーザー等を使用して整地すればよい。 In the [rolling pressure], although it varies depending on the required compaction, it is desired to roll the rolling force about every 30 cm. Rolling is performed by agitation on the back of the backhoe bucket after stirring. Then step on the backhoe and use a vibrating roller for finishing. When the soil surface needs to be flattened, it may be leveled using a grader or bulltozer.

本発明の下記土壌固化処理剤を使用して、固化する土壌の目標強度を15トンブルドーザーが作業可能なコーン指数から5kgf/cm2と設定し, 一軸圧縮強度を求めると、処理後の一軸圧縮強度は1.0kgf/cm2となるので、目標とする添加量は2.1%となる。この基となる一軸圧縮試験の試験結果を表1に示す。 Using the following soil solidification treatment agent of the present invention, the target strength of the soil to be solidified is set to 5 kgf / cm 2 from the corn index at which the 15-ton bulldozer can work, and the uniaxial compression strength is determined. Since the strength is 1.0 kgf / cm 2 , the target addition amount is 2.1%. Table 1 shows the test results of the uniaxial compression test as the basis.

Figure 2005336232
Figure 2005336232

上記で使用の土壌固化処理剤の内容は以下の通りである。製紙スラッジ灰60-90 重量%、高炉セメント10-30 重量%を均一に混合した固化剤主剤[A剤]60-90 重量%と、硫酸アルミニウム10-20 重量%、高炉スラグ20-30 重量%、硫酸カルシウム40-60 重量%、二酸化珪素10-20 重量%、炭酸ナトリウム10-20 重量%、硫酸ナトリウム10-20 重量%を混合した固化剤反応剤[B剤]10-40 重量%とからなる。   The contents of the soil solidifying agent used above are as follows. 60-90% by weight of paper sludge ash, 10-30% by weight of blast furnace cement, 60-90% by weight of solidifying agent (A), 10-20% by weight of aluminum sulfate, 20-30% by weight of blast furnace slag , Calcium sulfate 40-60 wt%, silicon dioxide 10-20 wt%, sodium carbonate 10-20 wt%, sodium sulfate 10-20 wt% mixed solidifying agent reactant [B agent] 10-40 wt% Become.

本発明の土壌固化処理剤は下記の分野に使用することができる。
(イ)官・民を問わず水資源の開発途上で発生する土壌処理の分野
(ロ)農業・農地・畜産業に関わる土壌・汚泥処理の分野
(ハ)上水・下水・工業用水処理の関連で発生する汚泥処理の分野
(ニ)法面の造成・修復等の応用分野
(ホ)本発明の土壌固化剤による処理土壌の水浸透性機能を生かした分野
(ヘ)緑化事業、グランド、スポーツ施設整備事業分野
(ト)遊歩道・公園・河川敷等の自然の道路を大事にする分野
The soil solidification treatment agent of the present invention can be used in the following fields.
(B) Fields of soil treatment generated during the development of water resources regardless of public or private sector (b) Fields of soil and sludge treatment related to agriculture, farmland, and livestock industry (c) Water treatment, sewage, and industrial water treatment Fields of sludge treatment generated in related fields (d) Fields of application such as slope construction and restoration (e) Fields utilizing the water permeability function of soil treated with the soil solidifying agent of the present invention (f) Greening project, ground, Sports facilities maintenance business field (G) Fields that take care of natural roads such as promenades, parks, riverbeds, etc.

Claims (1)

製紙スラッジ灰またはフライアッシュ60-90 重量%、高炉セメントまたはポルトランドセメント10-30 重量%を均一に混合した固化剤主剤[A剤]60-90 重量%と、硫酸アルミニウム10-20 重量%、高炉スラグ20-30 重量%、硫酸カルシウム40-60 重量%、二酸化珪素10-20 重量%、炭酸ナトリウム10-20 重量%、硫酸ナトリウム10-20 重量%を混合した固化剤反応剤[B剤]10-40 重量%とからなる土壌固化処理剤。 60-90% by weight of solidifying agent [agent A] in which paper sludge ash or fly ash 60-90% by weight, 10-30% by weight of blast furnace cement or Portland cement are uniformly mixed, 10-20% by weight of aluminum sulfate, blast furnace Solidifying agent reactant [B agent] mixed with 20-30 wt% slag, 40-60 wt% calcium sulfate, 10-20 wt% silicon dioxide, 10-20 wt% sodium carbonate, 10-20 wt% sodium sulfate 10 A soil solidification treatment agent consisting of -40% by weight.
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Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005344031A (en) * 2004-06-04 2005-12-15 Dc Co Ltd Soil improving material
JP2007160193A (en) * 2005-12-13 2007-06-28 Tatsutoshi Komatsu Rapid dewatering solidification agent for treatment of concentrated sludge having high water content
JP2012223733A (en) * 2011-04-21 2012-11-15 Hiroshima Univ Method for improving ambient water quality
JP2013064052A (en) * 2011-09-16 2013-04-11 Dc Co Ltd Soil conditioner
CN103723940A (en) * 2013-11-21 2014-04-16 浙江大学 Mucky soil composite curing agent and application
JP2015081265A (en) * 2013-10-21 2015-04-27 株式会社土地改良センター Heavy metal-coating solidifying agent
JP2020015850A (en) * 2018-07-26 2020-01-30 日本製鉄株式会社 Manufacturing method of calcia-modified soil
CN111423080A (en) * 2020-03-02 2020-07-17 南京市城市建设投资控股(集团)有限责任公司 Foundation excavation slurry stabilizing and curing agent and preparation and use method thereof
CN112321231A (en) * 2020-11-03 2021-02-05 江苏叁山生态环境发展有限公司 Formula and preparation method of polymer composite flowing type dredging sludge solidified soil
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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0739845A (en) * 1993-08-03 1995-02-10 Takeo Tsutsui Production of recycling materials from refuse incineration ashes, sewer sludge incineration ashes and the like
JPH07136693A (en) * 1993-11-22 1995-05-30 Koji Ogawa Sludge solidification agent
JPH1034125A (en) * 1996-07-29 1998-02-10 Yamashita Kenji Solidifying agent for sludge, organic soil, and harmful soil
JPH11106244A (en) * 1997-09-30 1999-04-20 Mitsubishi Materials Corp Cement composition

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0739845A (en) * 1993-08-03 1995-02-10 Takeo Tsutsui Production of recycling materials from refuse incineration ashes, sewer sludge incineration ashes and the like
JPH07136693A (en) * 1993-11-22 1995-05-30 Koji Ogawa Sludge solidification agent
JPH1034125A (en) * 1996-07-29 1998-02-10 Yamashita Kenji Solidifying agent for sludge, organic soil, and harmful soil
JPH11106244A (en) * 1997-09-30 1999-04-20 Mitsubishi Materials Corp Cement composition

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JP2005344031A (en) * 2004-06-04 2005-12-15 Dc Co Ltd Soil improving material
JP2007160193A (en) * 2005-12-13 2007-06-28 Tatsutoshi Komatsu Rapid dewatering solidification agent for treatment of concentrated sludge having high water content
JP4683638B2 (en) * 2005-12-13 2011-05-18 達利 小松 Rapid dehydrating solidifying agent for treatment of high water content concentrated sludge
JP2012223733A (en) * 2011-04-21 2012-11-15 Hiroshima Univ Method for improving ambient water quality
JP2013064052A (en) * 2011-09-16 2013-04-11 Dc Co Ltd Soil conditioner
JP2015081265A (en) * 2013-10-21 2015-04-27 株式会社土地改良センター Heavy metal-coating solidifying agent
CN103723940A (en) * 2013-11-21 2014-04-16 浙江大学 Mucky soil composite curing agent and application
JP2020015850A (en) * 2018-07-26 2020-01-30 日本製鉄株式会社 Manufacturing method of calcia-modified soil
JP7114385B2 (en) 2018-07-26 2022-08-08 日本製鉄株式会社 Method for producing calcia-improved soil
CN111423080A (en) * 2020-03-02 2020-07-17 南京市城市建设投资控股(集团)有限责任公司 Foundation excavation slurry stabilizing and curing agent and preparation and use method thereof
CN111423080B (en) * 2020-03-02 2022-09-16 南京市城市建设投资控股(集团)有限责任公司 Foundation excavation slurry stabilizing and curing agent and preparation and use method thereof
CN112321231A (en) * 2020-11-03 2021-02-05 江苏叁山生态环境发展有限公司 Formula and preparation method of polymer composite flowing type dredging sludge solidified soil
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