JP3488975B2 - Composition for soil stabilization treatment - Google Patents

Composition for soil stabilization treatment

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Publication number
JP3488975B2
JP3488975B2 JP23740896A JP23740896A JP3488975B2 JP 3488975 B2 JP3488975 B2 JP 3488975B2 JP 23740896 A JP23740896 A JP 23740896A JP 23740896 A JP23740896 A JP 23740896A JP 3488975 B2 JP3488975 B2 JP 3488975B2
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JP
Japan
Prior art keywords
composition
sample
soil
soil stabilization
reaction
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
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JP23740896A
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Japanese (ja)
Other versions
JPH09157648A (en
Inventor
輝男 浦野
健 渡辺
寛 宮路
Original Assignee
村樫石灰工業株式会社
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  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は軟弱地盤の土質安定
処理に用いられる組成物に関する。特に高含水比の軟弱
土、汚泥等の土の固化に効果のある土質安定処理用組成
物を提供する。
TECHNICAL FIELD The present invention relates to a composition used for soil stabilization treatment of soft ground. In particular, the present invention provides a composition for stabilizing soil, which is effective for solidifying soil such as soft soil having a high water content and sludge.

【0002】[0002]

【従来の技術】土質安定処理に用いられる組成物とは、
軟弱地盤に添加することによって土粒子とイオン交換反
応、ポゾラン反応等を生じ、土の力学的及び水理学的性
質を改善するものであり、従来より関東ロームや粘性土
土壌には石灰系組成物、シルトや砂質系土壌にはセメン
ト系組成物が主として用いられている。さらに、高有機
質土や高含水比の汚泥には、前記組成物では添加量が多
く必要になり、場合によっては実用に適さない状況にな
ることもある。このような場合には、生石灰又はセメン
トに、高炉水砕スラグ、フライアッシュ等のボゾラン
材、石膏、硫酸ソーダ等のセメント水和の刺激材を混合
した複合系の組成物、もしくはアウイン系焼成物(3C
aO・3Al23 ・CaSO4 )又はアルミナセメン
ト系化合物等の強度増進材を主体とした特殊セメント系
組成物が使用されている。
2. Description of the Related Art The composition used for soil stabilization is
When added to soft ground, it causes ion exchange reaction with soil particles, pozzolanic reaction, etc., and improves mechanical and hydraulic properties of soil. Cement-based compositions are mainly used for silt and sandy soil. Further, in the above composition, a large amount of addition is required for high organic soil or sludge having a high water content, and in some cases, it may not be suitable for practical use. In such a case, quick lime or cement, granulated blast furnace slag, bozolan material such as fly ash, gypsum, composite composition of a mixture of cement hydration stimulants such as sodium sulphate, or a fired fired material (3C
aO · 3Al 2 O 3 · CaSO 4) or special cementitious composition mainly containing strength enhancing material alumina cement-based compounds have been used.

【0003】しかしながら、アウイン系組成物又はアル
ミナセメント系化合物を主成分とする特殊セメント系組
成物は、アウイン系組成物やアルミナセメントが高温焼
成により製造されるため、必然的に高価にならざるを得
ない欠点を有している。また施工面においても、深層混
合工法や表層混合で湿式工法を採用する場合は、アウイ
ン系化合物は水の存在下で急結硬化性を呈するため、土
壌との混合中にゲル化を生じ作業性の悪化や混合不良の
状態となる。これらの欠陥を補うため凝結遅延剤を添加
する方法も採られているが、添加量の設定に複雑な操作
を必要とし、且つコストアップの要因となっている。
[0003] However, the Auin composition or the special cement composition containing an alumina cement compound as a main component is necessarily expensive because the Auin composition and the alumina cement are produced by high temperature firing. It has drawbacks that cannot be obtained. Also in terms of construction, when adopting the wet mixing method in the deep layer mixing method or the surface layer mixing, the hain compound exhibits rapid hardening in the presence of water, so that gelation occurs during mixing with soil and workability is improved. Deterioration and poor mixing. A method of adding a setting retarder to compensate for these defects has been adopted, but it requires a complicated operation to set the amount of addition and causes a cost increase.

【0004】[0004]

【発明が解決しようとする課題】本発明は、高価なアウ
イン系化合物やアルミナセメント系化合物を用いること
なく、高含水比の軟弱土、汚泥に対して通常のセメント
や、生石灰、消石灰よりも土質安定効果のある安価な組
成物を提供することを目的とする。
DISCLOSURE OF THE INVENTION The present invention does not use expensive hain-based compounds or alumina cement-based compounds, and is more suitable for soft soil with a high water content and sludge than ordinary cement, quicklime, and slaked lime. It is an object to provide an inexpensive composition having a stable effect.

【0005】[0005]

【課題を解決するための手段】本発明にかかわる土質安
定処理用組成物は、3CaO・Al23 ・6H2
(以下C3 AH6 と略記する)を300℃以上で熱分解
した生成物と生石灰の混合物であることを特徴とする。
The composition for soil stabilization according to the present invention is 3CaO.Al 2 O 3 .6H 2 O.
(Hereinafter abbreviated as C 3 AH 6 ) is characterized by being a mixture of a product obtained by thermally decomposing at 300 ° C. or higher and quick lime.

【0006】C3 AH6 を300℃以上で分解した場合
12CaO・7Al23 ・H2 O(以下C127 Hと
略記する)と若干の遊離石灰が生成することは公知であ
る。C127 Hは水と混合すると再水和しC3 AH6
生成することに着目し検討を重ねた結果、C3 AH6
熱分解生成物に生石灰を添加し混合することで高含水比
の軟弱土や汚泥処理用の組成物として優れた強度発現効
果を示すことを見いだして本発明を完成した。以下本発
明について詳細に説明する。
It is known that when C 3 AH 6 is decomposed at 300 ° C. or higher, 12CaO.7Al 2 O 3 .H 2 O (hereinafter abbreviated as C 12 A 7 H) and some free lime are formed. As a result of repeated studies paying attention to the fact that C 12 A 7 H is rehydrated when mixed with water to form C 3 AH 6, as a result of adding and mixing quick lime to the thermal decomposition product of C 3 AH 6 , and mixing it The present invention has been completed by finding that it exhibits an excellent strength developing effect as a composition for treating soft soil having a water content ratio and sludge. The present invention will be described in detail below.

【0007】先ずC3 AH6 の合成について説明し、次
いでC3 AH6 の熱分解反応について説明する。C3
6 は、Al(OH)3 とCaO又はCa(OH)2
水を加えて混合することにより簡単に合成できる。反応
式は、 2Al(OH)3 +3CaO+3H2 O→3CaO・A
23 ・6H2 O 又は、 2Al(OH)3 +3Ca(OH)2 →3CaO・Al
23 ・6H2 O である。次いで、得られたC3 AH6 を300℃以上に
加熱し、C127 HとCaO又はCa(OH)2 とに分
解する。反応式は、300〜500℃で、 7C3 AH6 →C127 H+9Ca(OH)2 +32H
2 O↑ 500℃以上で、 C127 H+9Ca(OH)2 →C127 H+9CaO
+9H2 O↑ であり、これらの反応式に従って、C127 Hと、Ca
O又はCa(OH)2 との混合物を得ることができる。
First, the synthesis of C 3 AH 6 will be described, and then the thermal decomposition reaction of C 3 AH 6 will be described. C 3 A
H 6 can be easily synthesized by adding water to Al (OH) 3 and CaO or Ca (OH) 2 and mixing them. The reaction formula is 2Al (OH) 3 + 3CaO + 3H 2 O → 3CaO · A
l 2 O 3 · 6H 2 O or 2Al (OH) 3 + 3Ca (OH) 2 → 3CaO · Al
A 2 O 3 · 6H 2 O. Next, the obtained C 3 AH 6 is heated to 300 ° C. or higher and decomposed into C 12 A 7 H and CaO or Ca (OH) 2 . The reaction formula is 300 to 500 ° C., 7C 3 AH 6 → C 12 A 7 H + 9Ca (OH) 2 + 32H
2 O ↑ Above 500 ° C, C 12 A 7 H + 9Ca (OH) 2 → C 12 A 7 H + 9CaO
+ 9H 2 O ↑, and according to these reaction formulas, C 12 A 7 H and Ca
It is possible to obtain a mixture with O or Ca (OH) 2 .

【0008】[0008]

【発明の実施の形態】Al源として使用する水酸化アル
ミニウムは、アルミニウムを水酸化アルミニウムの形で
含有しているものであれば特に限定はしないが、安価で
大量に入手できることからアルミスラッジが最適であ
る。アルミスラッジは、主としてアルミニウム製品の表
面処理工程でできるアルミニウム塩類を多量に含有した
廃液を中和して排水する際に副生するスラッジであり、
多量の水酸化アルミニウムを多くはゲル状の形で含有し
ている。従って水酸化アルミニウム以外にも不純物を多
少含むため、一部はセメント等の窯業原料として利用さ
れているが、殆どは産業廃棄物として埋め立て処分され
ているのが現状であり、用途開発が望まれている。ま
た、CaO又はCa(OH)2 源については、通常市販
されている生石灰又は消石灰が原料として使用できる。
BEST MODE FOR CARRYING OUT THE INVENTION The aluminum hydroxide used as the Al source is not particularly limited as long as it contains aluminum in the form of aluminum hydroxide, but aluminum sludge is most suitable because it is inexpensive and available in large quantities. Is. Aluminum sludge is a sludge produced as a by-product when neutralizing and draining a waste liquid containing a large amount of aluminum salts formed mainly in the surface treatment process of aluminum products,
It contains a large amount of aluminum hydroxide, mostly in gel form. Therefore, some impurities are included in addition to aluminum hydroxide, so some of them are used as ceramic raw materials such as cement, but most of them are currently landfilled as industrial wastes, and development of applications is desired. ing. As the CaO or Ca (OH) 2 source, commercially available quicklime or slaked lime can be used as a raw material.

【0009】両者の反応は、反応式に従って常温で反応
させることも可能であるが、反応を促進するため、50
〜100℃程度に加温する方法が望ましい。またアルミ
スラッジは通常水分を20〜100%(外比)含んだ状
態で産出されるので、生石灰を添加し脱水を兼ねた反応
をさせることも可能であるし、アルミスラッジに更に水
分を添加し、スラリー状にしてから消石灰又は生石灰を
添加し、反応を早く完結させる方法も考えられる。
The reaction between the two may be carried out at room temperature according to the reaction formula, but in order to accelerate the reaction, 50
A method of heating to about 100 ° C is desirable. Also, since aluminum sludge is usually produced in a state of containing 20 to 100% (external ratio) of water, it is possible to add quick lime for a reaction that also serves as dehydration, and to add more water to aluminum sludge. Alternatively, a method in which slaked lime or quick lime is added after forming a slurry to complete the reaction quickly can be considered.

【0010】次に反応して得られたC3 AH6 の熱分解
反応について述べる。C3 AH6 は前記の反応式に従っ
て、300℃を越えるとC127 HとCa(OH)2
に、更に500℃を越えるとCa(OH)2 がCaOに
容易に分解される。300℃以下ではC3 AH6 の分解
反応が進まないので本発明で使用する分解生成物は得ら
れない。また500℃を越えてもC127 Hの分解反応
の始まる1000℃付近まで状態変化が起こらない。
Next, the thermal decomposition reaction of C 3 AH 6 obtained by the reaction will be described. According to the above reaction formula, C 3 AH 6 becomes C 12 A 7 H and Ca (OH) 2 when it exceeds 300 ° C.
Moreover, when the temperature exceeds 500 ° C., Ca (OH) 2 is easily decomposed into CaO. Below 300 ° C., the decomposition reaction of C 3 AH 6 does not proceed, so the decomposition product used in the present invention cannot be obtained. Further, even if the temperature exceeds 500 ° C., the state does not change up to around 1000 ° C. at which the decomposition reaction of C 12 A 7 H starts.

【0011】C3 AH6 の熱分解生成物は水と反応して
速やかにC3 AH6 にもどり脱水と強度発現効果を呈す
るので、このままの状態でも土質安定処理用組成物とし
ての性能は優れている(後記の比較例1参照)。しかし
本発明者等は更にその性能を向上させる研究を続けた結
果、C3 AH6 の熱分解生成物に更に生石灰を適量添加
混合することによって軟弱土、汚泥等の土質安定処理用
組成物としての強度発現が遥かに良好になることを発見
するに至った。この場合添加量は、C3 AH6の熱分解
生成物100重量部に対して、生石灰の添加量が10〜
200重量部、好ましくは20〜150重量部程度が適
量であり殆どの土質に適応する。添加量が10重量部以
下の場合は添加効果が少なく、添加量が200重量部以
上になるとC3 AH6 の熱分解生成物の土質安定処理性
能を旨く発揮しなくなる。更に実際の使用においては、
本発明の土質安定処理用組成物にフライアッシュ、石
粉、水溶性高分子、高吸水性樹脂、下水汚泥焼却灰等を
添加して脱水性の向上や固化速度の調整をはかることも
可能である。本発明の組成物の添加量は対象土1立方メ
ートル(m3 )当り20〜200kgの範囲が適当であ
る。以下実施例によって本発明組成物の具体例及びその
効果を説明するが、本発明は下記の実施例に限定される
ものではない。
The thermal decomposition product of C 3 AH 6 reacts with water to quickly return to C 3 AH 6 to exhibit dehydration and strength development effects, so that the performance as a soil stabilization composition is excellent even in this state. (See Comparative Example 1 below). However, as a result of continuing the research for further improving the performance, the inventors of the present invention obtained a composition for soil stabilization treatment of soft soil, sludge, etc. by adding and mixing an appropriate amount of quicklime to the thermal decomposition product of C 3 AH 6. It has been discovered that the strength development of is much better. In this case, the amount of quick lime added is 10 to 100 parts by weight of the thermal decomposition product of C 3 AH 6.
An appropriate amount is 200 parts by weight, preferably 20 to 150 parts by weight, which is suitable for most soil types. If the addition amount is 10 parts by weight or less, the addition effect is small, and if the addition amount is 200 parts by weight or more, the soil stabilization treatment performance of the thermal decomposition product of C 3 AH 6 cannot be exhibited well. Furthermore, in actual use,
It is also possible to add fly ash, stone powder, a water-soluble polymer, a highly water-absorbent resin, sewage sludge incineration ash, etc. to the soil stabilization composition of the present invention to improve the dehydration property and adjust the solidification rate. . The addition amount of the composition of the present invention is appropriately in the range of 20 to 200 kg per 1 cubic meter (m 3 ) of the target soil. The following will describe specific examples of the composition of the present invention and the effects thereof by examples, but the present invention is not limited to the following examples.

【0012】[0012]

【比較例1】アジテーター付きステンレス反応器(容量
30L)に、表1に示した成分のアルミスラッジ7.6
3kg、生石灰(CaO含有量92.3%)6.14k
g及び清水20Lを入れ50℃で24時間撹拌しながら
反応させた。反応後の組成物を粉末X線回折により調査
したところ、C3 AH6 の生成を確認した。反応物を脱
水した後、電気炉で350℃で3時間加熱し熱分解を行
ないC127 HとCa(OH)2 の混合物10.0kg
を得た。得られたC127 HとCa(OH)2の混合物
をディスクミルにより粉砕し1mm篩全通、0.6mm
篩74.8%通過、0.15mm篩56.3%通過の粒
度に調整したものを試料Aとした。
[Comparative Example 1] Aluminum sludge of the components shown in Table 1 was added to a stainless reactor equipped with an agitator (capacity: 30 L).
3kg, quicklime (CaO content 92.3%) 6.14k
g and 20 L of fresh water were added and the reaction was carried out at 50 ° C. for 24 hours with stirring. When the composition after the reaction was examined by powder X-ray diffraction, formation of C 3 AH 6 was confirmed. After dehydrating the reaction product, it was heated in an electric furnace at 350 ° C. for 3 hours to be thermally decomposed, and a mixture of C 12 A 7 H and Ca (OH) 2 10.0 kg
Got The resulting mixture of C 12 A 7 H and Ca (OH) 2 was crushed by a disc mill and passed through a 1 mm sieve, 0.6 mm
Sample A was adjusted to have a particle size of 74.8% through a sieve and 56.3% through a 0.15 mm sieve.

【0013】[0013]

【表1】 [Table 1]

【0014】[0014]

【実施例1】試料A800gに生石灰(CaO含有量9
2.3%)200gを添加混合した組成物を製造し試料
Bとした。
[Example 1] Quick lime (CaO content 9
(2.3%) 200 g was added to and mixed with the composition to prepare Sample B.

【0015】[0015]

【比較例2】試料A800gに消石灰(工業用消石灰J
IS1号品)200gを添加混合した組成物を製造し試
料Cとした。
[Comparative Example 2] Slaked lime (industrial slaked lime J
A composition in which 200 g of IS1 product) was added and mixed was manufactured to be a sample C.

【0016】[0016]

【比較例3】試料A800gに普通ポルトランドセメン
ト200gを添加混合した組成物を製造し試料Dとし
た。
[Comparative Example 3] A sample A was prepared by mixing 200 g of ordinary Portland cement with 800 g of sample A to prepare a sample D.

【0017】[0017]

【比較例4】試料A800gに二水石膏200gを添加
混合した組成物を製造し試料Eとした。
[Comparative Example 4] A sample E was prepared by adding 200 g of gypsum dihydrate to 800 g of sample A to prepare a composition.

【0018】[0018]

【比較例5】公知の土質安定処理組成物である消石灰
(工業用消石灰JIS1号品)を試料Fとした。
[Comparative Example 5] Slaked lime (industrial slaked lime JIS No. 1 product), which is a known soil stabilization composition, was used as Sample F.

【0019】[0019]

【比較例6】公知の土質安定処理組成物である生石灰
(CaO含有量92.3%)を試料Fとした。
[Comparative Example 6] Quick lime (CaO content 92.3%), which is a known soil stabilization composition, was used as Sample F.

【0020】[0020]

【試験例1】試料A〜Gのそれぞれを、含水比109%
の関東ロームに対して100kg/m3 の割合で添加し
土質安定処理を行なった。土質安定処理の評価は「セメ
ント系組成物による安定処理土の試験方法」により、1
日後、3日後及び7日後の一軸圧縮強度を測定した。結
果を表2に示す。
[Test Example 1] Each of Samples A to G has a water content ratio of 109%.
A soil stabilization treatment was carried out by adding 100 kg / m 3 to Kanto loam. Soil stabilization is evaluated by "Test method of stabilized soil with cement composition" according to 1
The uniaxial compressive strength was measured after 3 days and 7 days. The results are shown in Table 2.

【0021】[0021]

【表2】 [Table 2]

【0022】表2から明らかなように、C3 AH6 の熱
分解生成物(粒度調整品)単独(試料A)、又は生石灰
単独(試料F)を使用した場合に比べて、試料Aと生石
灰の混合物(混合重量比8:2)である試料B(実施例
1)を使用した場合は、一軸圧縮強度が向上して、優れ
た土質安定処理効果を示している。また添加物として消
石灰(試料C)、セメント(試料D)、二水石膏(試料
E)場合に比べても、生石灰を添加した効果はぬきんで
ている。
As is clear from Table 2, as compared with the case where the thermal decomposition product of C 3 AH 6 (particle size adjusted product) alone (Sample A) or quick lime alone (Sample F) is used, Sample A and quick lime are used. When the sample B (Example 1) which is the mixture (mixing weight ratio 8: 2) is used, the uniaxial compressive strength is improved, and the excellent soil stabilization treatment effect is exhibited. Moreover, the effect of adding quick lime as an additive is clear compared to the cases of slaked lime (Sample C), cement (Sample D), and gypsum dihydrate (Sample E).

【0023】[0023]

【比較例7】容量5Lのステンレスビーカーに、表3に
示した成分のアルミスラッジ1.9kg、生石灰(Ca
O含有量92.3%)1.2kg及び50℃の温水3L
を加えスラリーとし、50℃に保温しながら撹拌機で2
時間混合した。混合終了後、室温で24時間放置し、吸
引濾過により固形分を分離し、分離した固形分を乾燥機
中で110℃、3時間乾燥し、C3 AH6 含有物2.7
kgを得た。更にこれを電気炉で550℃で3時間加熱
して熱分解を行ない、C127 HとCaOの混合物2.
0kgを得た。得られたC127 HとCaOの混合物
を、振動ミルにより粉砕し、1mm篩全通、0.6mm
篩75.7%通過、0.15mm篩58.5%通過の粒
度に調整し試料Hとした。
Comparative Example 7 A stainless beaker having a capacity of 5 L was charged with 1.9 kg of aluminum sludge having the components shown in Table 3 and quick lime (Ca).
O content 92.3%) 1.2 kg and 50 L of warm water 3 L
Is added to form a slurry, and the mixture is kept at 50 ° C with a stirrer to
Mixed for hours. After the completion of mixing, the mixture was left standing at room temperature for 24 hours, the solid content was separated by suction filtration, and the separated solid content was dried in a dryer at 110 ° C. for 3 hours to obtain a C 3 AH 6 -containing material 2.7.
I got kg. Further, this was heated in an electric furnace at 550 ° C. for 3 hours for thermal decomposition, and a mixture of C 12 A 7 H and CaO 2.
0 kg was obtained. The obtained mixture of C 12 A 7 H and CaO was crushed by a vibration mill, and then passed through a 1 mm sieve, 0.6 mm
Sample H was prepared by adjusting the particle size so that it passes 75.7% of the sieve and 58.5% of the 0.15 mm sieve.

【0024】[0024]

【表3】 [Table 3]

【0025】[0025]

【実施例2】試料H500gに生石灰(CaO含有量9
2.3%)500gを添加混合した組成物を製造し試料
Iとした。
[Example 2] Quick lime (CaO content 9
(2.3%) 500 g was added and mixed to prepare a composition, which was designated as Sample I.

【0026】[0026]

【比較例8】試料H500gに普通ポルトランドセメン
ト500gを添加混合した組成物を製造し試料Jとし
た。
[Comparative Example 8] Sample J was prepared by preparing a composition in which 500 g of ordinary Portland cement was added and mixed with 500 g of sample H.

【0027】[0027]

【比較例9】試料H500gに消石灰(工業用消石灰J
IS1号品)500gを添加混合した組成物を製造し試
料Kとした。
[Comparative Example 9] Slaked lime (industrial slaked lime J
A composition in which 500 g of IS1 product) was added and mixed was manufactured to be a sample K.

【0028】[0028]

【試験例2】試料H〜Kのそれぞれを含水比135%の
火山灰質の建設汚泥に対して120kg/m3 の割合で
添加し土質安定処理を行なった。土質安定処理の評価は
試験例1同様に「セメント系組成物による安定処理土の
試験方法」により、1日後、3日後、及び7日後の一軸
圧縮強度を測定した。結果を表4に示す。
Test Example 2 Samples H to K were added to a volcanic ash construction sludge having a water content of 135% at a rate of 120 kg / m 3 to perform soil stabilization treatment. As for the evaluation of the soil stabilization treatment, the uniaxial compressive strength after 1 day, 3 days, and 7 days was measured by the “test method for stabilized soil with cement composition” as in Test Example 1. The results are shown in Table 4.

【0029】[0029]

【表4】 [Table 4]

【0030】表4から明らかなように、C3 AH6 の熱
分解生成物(粒度調整品)単独(試料H)、又は添加物
としてセメント(試料J)、消石灰(試料K)を使用し
た場合に比べて、生石灰を添加混合した組成物(試料
I)の土質安定処理効果はぬきんでている。
As is clear from Table 4, when the thermal decomposition product of C 3 AH 6 (particle size adjusted product) alone (Sample H) or cement (Sample J) or slaked lime (Sample K) was used as an additive. Compared with the above, the soil stabilization treatment effect of the composition (Sample I) to which quick lime was added and mixed is clear.

【0031】[0031]

【発明の効果】高含水比の軟弱土や汚泥に対して、従来
より使用されている土質安定処理用組成物よりも優れた
安定処理効果がえられ、施工上組成物の添加量の削減等
の経済的効果が期待される。
EFFECTS OF THE INVENTION It is possible to obtain a superior stabilizing effect to soft soil and sludge having a high water content ratio than the conventionally used soil stabilizing composition, and to reduce the addition amount of the composition for construction. The economic effect of is expected.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI C09K 17/06 C09K 17/06 P 17/10 17/10 P // C09K 103:00 103:00 (58)調査した分野(Int.Cl.7,DB名) C09K 17/08 C01F 7/16 C04B 7/32 C04B 7/34 C09K 17/02 C09K 17/06 C09K 17/10 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI C09K 17/06 C09K 17/06 P 17/10 17/10 P // C09K 103: 00 103: 00 (58) Fields investigated ( Int.Cl. 7 , DB name) C09K 17/08 C01F 7/16 C04B 7/32 C04B 7/34 C09K 17/02 C09K 17/06 C09K 17/10

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 3CaO・Al23 ・6H2 Oを30
0℃以上で熱分解した生成物と生石灰の混合物であるこ
とを特徴とする土質安定処理用組成物。
1. 30% of 3CaO.Al 2 O 3 .6H 2 O
A composition for soil stabilization, which is a mixture of a product pyrolyzed at 0 ° C or higher and quicklime.
【請求項2】 3CaO・Al23 ・6H2 Oを30
0℃以上で熱分解した生成物100重量部と生石灰10
〜200重量部の混合物である請求項1に記載の土質安
定処理用組成物。
2. 30% of 3CaO.Al 2 O 3 .6H 2 O
100 parts by weight of product pyrolyzed at 0 ° C. or higher and quick lime 10
The composition for soil stabilization according to claim 1, which is a mixture of about 200 parts by weight.
JP23740896A 1995-10-05 1996-09-09 Composition for soil stabilization treatment Expired - Lifetime JP3488975B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP23740896A JP3488975B2 (en) 1995-10-05 1996-09-09 Composition for soil stabilization treatment

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP7-258415 1995-10-05
JP25841595 1995-10-05
JP23740896A JP3488975B2 (en) 1995-10-05 1996-09-09 Composition for soil stabilization treatment

Publications (2)

Publication Number Publication Date
JPH09157648A JPH09157648A (en) 1997-06-17
JP3488975B2 true JP3488975B2 (en) 2004-01-19

Family

ID=26533192

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3488975B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5220946B1 (en) * 2012-09-25 2013-06-26 株式会社山陽テクノ Hydropyrogenic agent

Also Published As

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