JP3479715B2 - Soil solidifying agent - Google Patents

Soil solidifying agent

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Publication number
JP3479715B2
JP3479715B2 JP03846999A JP3846999A JP3479715B2 JP 3479715 B2 JP3479715 B2 JP 3479715B2 JP 03846999 A JP03846999 A JP 03846999A JP 3846999 A JP3846999 A JP 3846999A JP 3479715 B2 JP3479715 B2 JP 3479715B2
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JP
Japan
Prior art keywords
soil
weight
sulfate
solidifying agent
parts
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.)
Expired - Fee Related
Application number
JP03846999A
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Japanese (ja)
Other versions
JP2000239660A (en
Inventor
勝一 國松
豊 松田
Original Assignee
東成産業有限会社
豊 松田
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  • Processing Of Solid Wastes (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、例えばシールド工
法、地中連続壁工法、浚渫工法、表層および深層地盤改
良工法等の建設現場からの発生土のような土壌を固化さ
せるために使用される土壌固化剤に関するものである。
TECHNICAL FIELD The present invention is used for solidifying soil such as soil generated from a construction site such as a shield construction method, an underground continuous wall construction method, a dredging construction method, and a surface and deep ground improvement construction method. It relates to a soil solidifying agent.

【0002】[0002]

【発明の背景】上記建設現場からの発生土のような土壌
は水分を多量に含み流動性があり、そのまゝでは運搬、
輸送が困難である。そこで該土壌には土壌固化剤を添加
して固化させた上で運搬、輸送行なう方法が採られてい
る。
BACKGROUND OF THE INVENTION Soil such as the soil generated from the above construction sites contains a large amount of water and is fluid, and if it is transported,
Difficult to transport. Therefore, a method has been adopted in which a soil solidifying agent is added to the soil to solidify it, and then the soil is transported and transported.

【0003】[0003]

【従来の技術】従来、この種の土壌固化剤としては、セ
メント系固化剤、生石灰系固化剤、石膏系固化剤や有機
高分子系凝集剤等が使用されている。
2. Description of the Related Art Conventionally, cement-based solidifying agents, quicklime-based solidifying agents, gypsum-based solidifying agents, organic polymer-based flocculants and the like have been used as soil solidifying agents of this type.

【0004】[0004]

【発明が解決しようとする課題】上記セメント系固化剤
や生石灰系固化剤は、土壌に対して通常10〜15重量
%添加するが、このような添加量では処理土のpHが1
2以上になり、また運搬、輸送が可能な程度に固化する
までに長時間を要すると言う問題点がある。更に上記石
膏系固化剤では処理土は短時間で固化するが、水に接触
すると固化剤が溶解して処理土が崩壊してしまい、また
多量に水分を含む土壌の場合には固化不良を起こす。ま
た更に上記有機高分子系凝集剤でも固化時間は早いが処
理土は耐水性がなく、水に接触すると処理土が崩壊して
しまい、また水分を多量に含む土壌の場合には該有機高
分子系凝集剤の添加量が多くなり、処理土が弾性体とな
って、重機類で突崩したり搬出したりする作業が困難に
なる。
The above cement-based solidifying agent and quicklime-based solidifying agent are usually added in an amount of 10 to 15% by weight with respect to the soil. With such an addition amount, the pH of the treated soil is 1%.
There is a problem in that it takes 2 or more and it takes a long time to solidify to the extent that it can be transported and transported. Furthermore, with the above-mentioned gypsum-based solidifying agent, the treated soil solidifies in a short time, but when it comes into contact with water, the solidifying agent dissolves and the treated soil collapses, and in the case of soil containing a large amount of water, poor solidification occurs. . Furthermore, even with the above organic polymer-based coagulant, the treated soil does not have water resistance even though the solidification time is short, the treated soil will collapse when contacted with water, and in the case of soil containing a large amount of water, the organic polymer The amount of the system flocculant added increases, and the treated soil becomes an elastic body, which makes it difficult for the heavy machinery to break down or carry it out.

【0005】[0005]

【課題を解決するための手段】本発明はこのような建設
現場からの発生土のような土壌を短時間で運搬、輸送が
可能な程度に固化させることを課題とするものであり、
上記課題を解決するための手段として、酸化マグネシウ
ム100重量部と、硫酸アルミニウム、硫酸第1鉄、ポ
リ塩化アルミニウム、酸性硫酸ナトリウム、スルファミ
ン酸、ポリアクリル酸、硫酸アンモニウム、明ばん、仮
焼明ばん石、および硫酸亜鉛からなる群から選ばれた一
種または二種以上の固化剤10〜100重量部とからな
土壌固化剤を提供するものであり、また該酸化マグネ
シウム100重量部と該固化剤10〜100重量部と
らなる混合物には更に酸性剤5〜50重量%を添加する
ことが望ましい。また水分を多量に含む土壌の場合に
は、上記組成に更に有機高分子凝集剤および/または吸
水剤0.1〜2.0重量%を添加することが望ましい。
また上記土壌固化剤に更に固化促進剤を0.3〜10.
0重量%添加することが望ましく、該固化促進剤は水と
反応して炭酸ガスを発生することが出来る化合物および
/または多価金属塩であることが望ましい。
SUMMARY OF THE INVENTION An object of the present invention is to solidify soil such as soil generated from such a construction site so that it can be transported and transported in a short time.
As means for solving the above problems, 100 parts by weight of magnesium oxide, aluminum sulfate, ferrous sulfate, polyaluminum chloride, sodium acid sulfate, sulfamic acid, polyacrylic acid, ammonium sulfate, alum, calcined alum and Tona with one or 10 to 100 parts by weight of two or more solidifying agent selected from the group consisting of zinc sulfate
That it is intended to provide a soil solidifying agent, also or 100 parts by weight of magnesium oxide and solid agent 10 to 100 parts by weight
It is desirable further adding an acidic agent 5-50% by weight in Ranaru mixture. In the case of soil containing a large amount of water, it is desirable to add 0.1 to 2.0% by weight of an organic polymer coagulant and / or a water absorbing agent to the above composition.
Further, a solidification accelerator of 0.3 to 10.
It is desirable to add 0% by weight, and it is desirable that the solidification accelerator is a compound and / or a polyvalent metal salt capable of reacting with water to generate carbon dioxide gas.

【0006】[0006]

【発明の実施の形態】本発明に使用される酸化マグネシ
ウムには、低温焼成品と高温焼成品とがあるが、反応性
の点からみて低温焼成品(軽焼マグネシア)の使用が望
ましい。また本発明ではドロマイトのような酸化マグネ
シウムを含むものも使用出来る。
BEST MODE FOR CARRYING OUT THE INVENTION Magnesium oxide used in the present invention includes a low temperature calcined product and a high temperature calcined product, and it is preferable to use a low temperature calcined product (light burned magnesia) from the viewpoint of reactivity. In the present invention, a material containing magnesium oxide such as dolomite can also be used.

【0007】本発明の土壌固化剤には、上記酸化マグネ
シウムの他に、硫酸アルミニウム、硫酸第1鉄、ポリ塩
化アルミニウム、酸性硫酸ナトリウム、スルファミン
酸、ポリアクリル酸、硫酸アンモニウム、明ばん、仮焼
明ばん石、および硫酸亜鉛からなる群から選ばれた一種
または二種以上の化合物が使用される。上記化合物のう
ち、硫酸アルミニウム、ポリ塩化アルミニウム、酸性硫
酸ナトリウム、スルファミン酸、ポリアクリル酸、硫酸
アンモニウムは処理土のpHを低くする作用もある。
In addition to the above magnesium oxide, the soil solidifying agent of the present invention includes aluminum sulfate, ferrous sulfate, polyaluminum chloride, sodium acid sulfate, sulfamic acid, polyacrylic acid, ammonium sulfate, alum, and calcination. One or more compounds selected from the group consisting of albite and zinc sulfate are used. Among the above compounds , aluminum sulfate, polyaluminum chloride, sodium acid sulfate, sulfamic acid, polyacrylic acid, and ammonium sulfate also have the action of lowering the pH of the treated soil.

【0008】本発明では処理土のpHを低くするために
酸性剤を使用してもよい。該酸性剤としては、例えば粉
末硫酸、硼酸等の粉末状の無機酸あるいは蓚酸、クエン
酸、リンゴ酸、ベンゼンスルホン酸等の粉末状の有機
酸、硫酸アンモニウム、ベンゼンスルホン酸アンモニウ
ム等の強酸と弱塩基との粉末状の塩、塩化第2鉄、塩化
マグネシウム、塩化アンモニウム等の粉末状の酸性塩等
が使用される。
In the present invention, an acid agent may be used to lower the pH of the treated soil. Examples of the acidic agent include powdered inorganic acids such as powdered sulfuric acid and boric acid, or powdered organic acids such as oxalic acid, citric acid, malic acid, and benzenesulfonic acid, strong acids such as ammonium sulfate and ammonium benzenesulfonate, and weak bases. And a powdered salt of ferric chloride, a powdered acidic salt of ferric chloride, magnesium chloride, ammonium chloride, or the like.

【0009】処理する土壌の水分が例えば50重量%以
上の多量に含まれる場合には、有機高分子凝集剤および
/または吸水剤が使用される。上記有機高分子凝集剤と
しては、例えばポリアクリル酸ナトリウム、ポリアクリ
ルアミド、アクリル酸ナトリウム−アクリルアミド共重
合体、ポリエチレンオキサイドの合成高分子凝集剤、グ
アガム、キサンタンガム、アルギン酸等の天然高分子凝
集剤等があり、吸水剤としては例えば下水焼却灰、木
炭、活性炭、シリカゲル等がある。
When the soil to be treated contains a large amount of water such as 50% by weight or more, an organic polymer flocculant and / or a water absorbing agent is used. Examples of the organic polymer flocculant include sodium polyacrylate, polyacrylamide, sodium acrylate-acrylamide copolymer, synthetic polymer flocculant of polyethylene oxide, natural polymer flocculant such as guar gum, xanthan gum, and alginic acid. There are, for example, sewage incineration ash, charcoal, activated carbon and silica gel as the water absorbing agent.

【0010】本発明では処理土の固化を促進するために
更に固化促進剤を添加してもよい。該固化促進剤として
は、炭酸ナトリウム、重炭酸ナトリウム、炭酸カリ、重
炭酸カリ、エチレンカーボネート、イソシアナート化合
物等の水と反応して炭酸ガスを発生することが出来る化
合物(固化促進剤A)および/または塩化カルシウム、
塩化マグネシウム等の多価金属塩(固化促進剤B)等が
使用される。該固化促進剤Aは上記酸性剤と併用する
と、処理土のpHが高い場合でも、容易にpHを低くす
ることが出来るので、酸性助剤としても使用出来る。
In the present invention, a solidification accelerator may be further added to accelerate the solidification of the treated soil. Examples of the solidification accelerator include sodium carbonate, sodium bicarbonate, potassium carbonate, potassium bicarbonate, ethylene carbonate, a compound capable of reacting with water to generate carbon dioxide gas (solidification accelerator A), and the like. / Or calcium chloride,
A polyvalent metal salt such as magnesium chloride (solidification accelerator B) or the like is used. When the solidification accelerator A is used in combination with the above-mentioned acidifying agent, the pH can be easily lowered even when the pH of the treated soil is high, and therefore the solidifying accelerator A can be used also as an acid aid.

【0011】上記成分においては、上記酸化マグネシウ
ムと上記化合物と土壌との固化反応によって土壌が固化
せしめられるが、所望なれば酸性剤によって土壌のpH
を酸性側、望ましくはpH5〜9、更に望ましくはpH
5.8〜8.6に調節して該酸化マグネシウムと該化合
と土壌との固化反応を促進する。また水分を多量に含
有する土壌の場合には、上記成分に加えて上記有機高分
子凝集剤および/または吸水剤を添加すると、土壌が凝
縮して水が排除され、あるいは土壌中の水が吸収され、
望ましい固さの土壌固化物が得られる。上記成分以外
に、所望なれば炭酸カルシウム、無水石膏、半水石膏、
タルク、未焼ドロマイト、ケイ石粉等の充填材が添加さ
れてもよい。
[0011] In the above components, although the soil by solidification reaction of the magnesium oxide and the compound and soil is solidify, pH of the soil by and if desired, an acidic agent
On the acidic side, preferably pH 5-9, more preferably pH
5.8 to 8.6 and the magnesium oxide and the compound
It promotes the solidification reaction between objects and soil. In addition, in the case of soil containing a large amount of water, if the organic polymer flocculant and / or water absorbing agent is added in addition to the above components, the soil is condensed and water is removed or water in the soil is absorbed. Is
A soil solidified product having a desired hardness is obtained. In addition to the above components, if desired, calcium carbonate, anhydrous gypsum, hemihydrate gypsum,
Fillers such as talc, unburned dolomite and silica powder may be added.

【0012】上記成分の添加比率は本発明の土壌固化剤
においては、酸化マグネシウム100重量部に対して上
化合物は10〜100重量部添加され、そして所望な
れば該土壌固化剤中に上記酸性剤は5〜50重量%添加
されるが、該酸性剤は土壌のpHに応じて添加量を調節
すべきであることは言うまでもない。また有機高分子凝
集剤および/または吸水剤は0.1〜2.0重量%の範
囲で添加されるが、この添加量は土壌の水分含有量に応
じて調節される。更に上記固化促進剤は0.3〜10.
0重量%の範囲で添加されるが、該固化促進剤はA,B
併用されることが望ましい。更に充填材は通常25〜5
00重量%の範囲で添加される。
In the soil solidifying agent of the present invention, the addition ratio of the above components is such that 10 to 100 parts by weight of the above compound is added to 100 parts by weight of magnesium oxide, and the desired ratio is obtained.
Then , the above-mentioned acidifying agent is added to the soil solidifying agent in an amount of 5 to 50% by weight, but it goes without saying that the addition amount of the acidifying agent should be adjusted according to the pH of the soil. The organic polymer coagulant and / or the water absorbing agent is added in the range of 0.1 to 2.0% by weight, and the addition amount is adjusted according to the water content of soil. Further, the solidification accelerator is 0.3-10.
The solidification accelerator is added in the range of 0% by weight.
It is desirable to use them together. Further, the filler is usually 25 to 5
It is added in the range of 00% by weight.

【0013】本発明の土壌固化剤は土壌に添加する前に
全成分を混合し、その後土壌に添加されてもよいし、ま
た各成分を個々に土壌に添加されてもよいし、更に成分
のうちの二種以上をあらかじめ混合しておいて土壌に添
加されてもよい。
The soil solidifying agent of the present invention may be added to the soil after mixing all the components before adding to the soil, or each component may be added individually to the soil. Two or more of them may be mixed in advance and added to the soil.

【0014】本発明の土壌固化剤の土壌に対する添加量
は、土質、含水量等によって調節される。一般に粘性の
大きな土質(粘土質)の場合には添加量は少なくして良
く、また粘性の小さな土質(砂質)の場合には添加量は
多くする。更に含水量の大きい土壌の場合は添加量は多
くし、含水量の小さい土壌の場合には添加量は少なくす
る。一般的に言えば含水量80〜100重量%の土壌の
場合には、本発明の土壌固化剤は土壌1m当たり30
〜100kg程度添加され、含水量100〜200重量
%の土壌の場合には、本発明の土壌固化剤は土壌1m
当たり50〜200kg程度添加される。
The amount of the soil-solidifying agent of the present invention added to soil is adjusted depending on the soil quality, water content and the like. Generally, the amount of addition may be small in the case of highly viscous soil (clay), and may be increased in the case of low viscosity soil (sand). Further, the addition amount is increased in the case of soil having a high water content, and the addition amount is decreased in the case of soil having a low water content. Generally speaking, in the case of soil having a water content of 80 to 100% by weight, the soil solidifying agent of the present invention is 30 per 1 m 3 of soil.
˜100 kg, and in the case of soil having a water content of 100 to 200% by weight, the soil solidifying agent of the present invention is 1 m 3 of soil.
About 50 to 200 kg is added per unit.

【0015】〔実施例1〕 地下鉄工事で発生した粘土質土壌(含水率47重量%、
含水比89重量%、一軸圧縮強度0kg/cm、pH
7.8)1000ccに対し、軽焼酸化マグネシウム1
00重量部、硫酸アルミニウム20重量部の混合物に1
0重量%の粉末酸性硫酸ナトリウムを添加した土壌固化
剤40gを添加し攪拌混合した。該土壌を気中養生した
場合の固化状況を表1に示す。
[Example 1] Clay soil generated by subway construction (water content 47% by weight,
Water content 89% by weight, uniaxial compressive strength 0 kg / cm 2 , pH
7.8) 1000 cc of light burned magnesium oxide 1
1 to a mixture of 00 parts by weight and 20 parts by weight of aluminum sulfate
40 g of a soil solidifying agent containing 0% by weight of powdered sodium acid sulfate was added and mixed with stirring. Table 1 shows the solidification status when the soil was cured in air.

【0016】[0016]

【表1】 表1によれば、該土壌は3時間後には搬出に支障ない程
度に固化し、更に7日後にはpH値が水質基準の上限
8.6を下回った。7日間気中養生した該土壌を水中に
投下した所、3日後でも崩壊はみられなかった。
[Table 1] According to Table 1, the soil was solidified after 3 hours to such an extent that it would not hinder the carry-out, and after 7 days, the pH value was below the upper limit of the water quality standard of 8.6. When the soil cured in the air for 7 days was dropped into water, no collapse was observed even after 3 days.

【0017】〔実施例2〕 トンネル工事で発生した砂質シルト土壌(含水率63重
量%、含水比170重量%、一軸圧縮強度0kg/cm
、pH6.7)1000ccに対し、軽焼酸化マグネ
シウム100重量部、ポリ塩化アルミニウム20重量部
の混合物に45重量%の半水石膏を添加した土壌固化剤
50gを添加し攪拌混合した。該土壌を気中養生した場
合の固化状況を表2に示す。
[Example 2] Sandy silt soil generated during tunnel construction (water content: 63% by weight, water content: 170% by weight, uniaxial compressive strength: 0 kg / cm)
50 g of a soil solidifying agent to which 45 wt% of hemihydrate gypsum was added to a mixture of 100 parts by weight of light-burned magnesium oxide and 20 parts by weight of polyaluminum chloride was added to 1000 cc of 2 , pH 6.7) and stirred and mixed. Table 2 shows the state of solidification when the soil was cured in air.

【0018】[0018]

【表2】 表2によれば、該土壌は直後でも搬出に支障ない程度に
固化し、更に8時間後にはpH値が水質基準の上限8.
6を下回った。24時間気中養生した該土壌を水中に投
下した所、3日後でも崩壊はみられなかった。
[Table 2] According to Table 2, the soil was solidified even immediately afterward so as not to hinder the carry-out, and after 8 hours, the pH value reached the upper limit of 8.
Fell below 6. When the soil aged in air for 24 hours was dropped into water, no disintegration was observed even after 3 days.

【0019】〔実施例3〕 実施例2の土壌に水を加えて含水率67重量%、含水比
203重量%に調製した。該土壌1000ccに対し、
軽焼酸化マグネシウム100重量部、明ばん50重量部
の混合物に50重量%の未焼ドロマイト、0.3重量%
のポリアクリル酸ナトリウムを添加した土壌固化剤50
gおよび100gを添加し攪拌混合した。該土壌を水中
養生した場合の固化状況(一軸圧縮強度(kg/c
)を表3に示す。
Example 3 Water was added to the soil of Example 2 to prepare a water content of 67% by weight and a water content ratio of 203% by weight. For 1000 cc of the soil,
50% by weight unburned dolomite, 0.3% by weight in a mixture of 100 parts by weight of light-burned magnesium oxide and 50 parts by weight of alum
Soil solidifying agent with added sodium polyacrylate 50
g and 100 g were added and mixed with stirring. Solidification status when the soil was cured in water (uniaxial compressive strength (kg / c
m 2 ) is shown in Table 3.

【0020】[0020]

【表3】 表3によれば、該土壌は土壌固化剤50g添加、100
g添加のいずれも1時間で搬出に支障ない程度に固化し
た。また8時間後のpH値は両者共に7.8であった。
24時間気中養生した該土壌を水中に投下した所、3日
後でも崩壊はみられなかった。
[Table 3] According to Table 3, the soil was added with 50 g of a soil solidifying agent, 100
All of the additions of g were solidified to the extent that they did not hinder the delivery in 1 hour. The pH value after 8 hours was 7.8 in both cases.
When the soil aged in air for 24 hours was dropped into water, no disintegration was observed even after 3 days.

【0021】〔実施例4〕 実施例1の土壌1000ccに軽焼酸化マグネシウム1
00重量部、硫酸第1鉄80重量部の混合物に50重量
%のケイ石粉と1重量%のエチレンカーボネートを添加
した土壌固化剤100gを添加し攪拌混合した。該土壌
を気中養生した場合の固化状況を表4に示す。
[Example 4] Light burned magnesium oxide 1 was added to 1000 cc of the soil of Example 1.
To a mixture of 00 parts by weight and 80 parts by weight of ferrous sulfate, 100 g of a soil solidifying agent containing 50% by weight of silica stone powder and 1% by weight of ethylene carbonate was added and mixed by stirring. Table 4 shows the solidification status when the soil was cured in air.

【0022】[0022]

【表4】 表4によれば、該土壌は20分後には搬出に支障ない程
度に固化し、pH値は水質基準の上限8.6を下回っ
た。24時間気中養生した該土壌を水中に投下した所、
3日後でも崩壊はみられなかった。
[Table 4] According to Table 4, after 20 minutes, the soil solidified to such an extent that it would not hinder the carrying out, and the pH value was below the upper limit of 8.6 of the water quality standard. When the soil that had been cured in the air for 24 hours was dropped into water,
No collapse was observed even after 3 days.

【0023】〔実施例5〕 浚渫工事から発生した有機質粘質土壌(含水率65重量
%、含水比186重量%、強熱加熱残分53重量%/c
、pH6.3)1000ccに軽焼酸化マグネシウ
ム100重量部、硫酸亜鉛50重量部、硫酸アルミニウ
ム15重量部の混合物に炭酸カルシウム30重量%、グ
アガム0.3重量%を添加した土壌固化剤150gを添
加し攪拌混合した。該土壌を水中養生した場合の固化状
況を表5に示す。
[Example 5] Organic viscous soil generated from dredging work (water content 65% by weight, water content ratio 186% by weight, ignition heating residue 53% by weight / c)
150 g of soil solidifying agent obtained by adding 30 parts by weight of calcium carbonate and 0.3% by weight of guar gum to a mixture of 100 parts by weight of light burned magnesium oxide, 50 parts by weight of zinc sulfate, and 15 parts by weight of aluminum sulfate in 1000 cc of m 2 , pH 6.3). Was added and mixed with stirring. Table 5 shows the solidification status when the soil was cured in water.

【0024】[0024]

【表5】 表5によれば、該土壌は5時間後には搬出に支障ない程
度に固化し、更に7日後のpH値は水質基準の上限8.
6を下回った。7日間水中養生した該土壌を水中に投下
した所、3日後でも崩壊はみられなかった。
[Table 5] According to Table 5, the soil solidifies after 5 hours to the extent that it does not hinder the removal, and the pH value after 7 days is the upper limit of the water quality standard of 8.
Fell below 6. When the soil, which had been cured in water for 7 days, was dropped into water, no disintegration was observed even after 3 days.

【0025】〔比較例1〕 実施例1の土壌1000ccに半水石膏を100gおよ
び200gを添加し攪拌混合した。該土壌を気中養生し
た場合の固化状況(一軸圧縮強度(kg/cm)を表
6に示す。
Comparative Example 1 100 g and 200 g of hemihydrate gypsum were added to 1000 cc of the soil of Example 1 and mixed with stirring. Table 6 shows the solidification state (uniaxial compressive strength (kg / cm 2 )) when the soil was cured in air.

【0026】[0026]

【表6】 該土壌固化剤を100g添加した土壌は、2時間後、2
00g添加した土壌は1時間後には搬出に支障のない程
度に固化し、また24時間後のpH値は8.0で水質基
準の上限8.6を下回ったが、24時間気中養生した該
土壌を水中に投下した所、1日後には崩壊がみられた。
[Table 6] The soil to which 100 g of the soil-solidifying agent was added was 2 hours later, and 2
The soil to which 00 g was added solidified after 1 hour to such an extent that there was no hindrance to carry-out, and the pH value after 24 hours was 8.0, which was below the upper limit of 8.6 of the water quality standard, but was cured in air for 24 hours. When the soil was dropped into water, it collapsed one day later.

【0027】〔比較例2〕 実施例3の土壌1000ccに対し、ポルトランドセメ
ント100重量部と硫酸アルミニウム100重量部の混
合物からなる土壌固化剤100gを添加し攪拌混合し
た。該土壌は直後の一軸圧縮強度が0.1kg/cm
であり、その後強度向上がみられず搬出困難な状態であ
った。
Comparative Example 2 To 1000 cc of the soil of Example 3, 100 g of a soil solidifying agent made of a mixture of 100 parts by weight of Portland cement and 100 parts by weight of aluminum sulfate was added and mixed with stirring. Immediately after that, the soil has a uniaxial compressive strength of 0.1 kg / cm 2
After that, the strength was not improved and it was difficult to carry out.

【0028】[0028]

【発明の効果】本発明の土壌固化剤は、土壌と混合して
短時間に運搬輸送の可能な程度に固化せしめることが出
来、また固化物は水との接触によっても崩壊せず、更に
重機類で容易に突崩すことが出来、建設現場での発生土
等の土壌の大量迅速処理が可能になる。また固化した土
壌のpH値を水質基準の上限8.6を下回るようにする
ことが出来るので、該土壌からの地下水や雨水等の滲出
水が周囲の環境へ悪影響を与えることもなく、植生に対
しても問題がない。したがって該土壌は再利用が可能で
ある。
Industrial Applicability The soil solidifying agent of the present invention can be mixed with soil and solidified to the extent that it can be transported and transported in a short time, and the solidified product does not collapse even when contacted with water, and the heavy equipment It can be easily broken down, and a large amount of soil such as soil generated at the construction site can be quickly processed. Further, since the pH value of the solidified soil can be set to be lower than the upper limit of 8.6 of the water quality standard, exuded water such as groundwater or rainwater from the soil does not adversely affect the surrounding environment and vegetation is prevented. There is no problem with it. Therefore, the soil can be reused.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI B09C 1/08 E02F 7/00 D C09K 17/08 C09K 103:00 17/48 B09B 3/00 304K E02F 7/00 ZAB C09K 103:00 (72)発明者 松田 豊 神奈川県横浜市緑区中山町908−29 (56)参考文献 特開 昭51−20414(JP,A) 特開 昭63−235392(JP,A) 特開 昭62−260753(JP,A) 特開 平10−316967(JP,A) (58)調査した分野(Int.Cl.7,DB名) C09K 17/02 B09B 3/00 B09C 1/08 C09K 17/08 C09K 17/48 E02F 7/00 C09K 103/00 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 7 Identification code FI B09C 1/08 E02F 7/00 D C09K 17/08 C09K 103: 00 17/48 B09B 3/00 304K E02F 7/00 ZAB C09K 103 : 00 (72) Inventor Yutaka Matsuda 908-29 Nakayama-cho, Midori-ku, Yokohama-shi, Kanagawa (56) Reference JP-A 51-20414 (JP, A) JP-A 63-235392 (JP, A) JP-A 62-260753 (JP, A) JP-A-10-316967 (JP, A) (58) Fields investigated (Int.Cl. 7 , DB name) C09K 17/02 B09B 3/00 B09C 1/08 C09K 17 / 08 C09K 17/48 E02F 7/00 C09K 103/00

Claims (5)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】酸化マグネシウム100重量部と、硫酸ア
ルミニウム、硫酸第1鉄、ポリ塩化アルミニウム、酸性
硫酸ナトリウム、スルファミン酸、ポリアクリル酸、硫
酸アンモニウム、明ばん、仮焼明ばん石、および硫酸亜
鉛からなる群から選ばれた一種または二種以上の固化剤
10〜100重量部とからなることを特徴とする土壌固
化剤
1. From 100 parts by weight of magnesium oxide, aluminum sulfate, ferrous sulfate, polyaluminum chloride, sodium acid sulfate, sulfamic acid, polyacrylic acid, ammonium sulfate, alum, calcined alum, and zinc sulfate. A soil solidifying agent comprising 10 to 100 parts by weight of one or more solidifying agents selected from the group consisting of
【請求項2】酸化マグネシウム100重量部と、硫酸ア
ルミニウム、硫酸第1鉄、ポリ塩化アルミニウム、酸性
硫酸ナトリウム、スルファミン酸、ポリアクリル酸、硫
酸アンモニウム、明ばん、仮焼明ばん石、および硫酸亜
鉛からなる群から選ばれた一種または二種以上の固化剤
10〜100重量部とからなる混合物に酸性剤5〜50
重量%を添加したことを特徴とする土壌固化剤
2. From 100 parts by weight of magnesium oxide, aluminum sulfate, ferrous sulfate, polyaluminum chloride, sodium acid sulfate, sulfamic acid, polyacrylic acid, ammonium sulfate, alum, calcined amber and zinc sulfate. acidic agent 5-50 in a mixture consisting of selected one or 10 to 100 parts by weight of two or more solidifying agent from the group consisting
Soil solidifying agent characterized by adding wt%
【請求項3】酸化マグネシウム100重量部と、硫酸ア
ルミニウム、硫酸第1鉄、ポリ塩化アルミニウム、酸性
硫酸ナトリウム、スルファミン酸、ポリアクリル酸、硫
酸アンモニウム、明ばん、仮焼明ばん石、および硫酸亜
鉛からなる群から選ばれた一種または二種以上の固化剤
10〜100重量部とからなる混合物に酸性剤5〜50
重量%および有機高分子凝集剤および/または吸水剤
0.1〜2.0重量%を添加したことを特徴とする土壌
固化剤
3. From 100 parts by weight of magnesium oxide, aluminum sulfate, ferrous sulfate, polyaluminum chloride, sodium acid sulfate, sulfamic acid, polyacrylic acid, ammonium sulfate, alum, calcined amber and zinc sulfate. acidic agent 5-50 in a mixture consisting of selected one or 10 to 100 parts by weight of two or more solidifying agent from the group consisting
% By weight and 0.1 to 2.0% by weight of an organic polymer flocculant and / or a water absorbing agent are added to the soil solidifying agent.
【請求項4】請求項1,2または3に記載の土壌固化剤
に更に固化促進剤を0.3〜10.0重量%添加したこ
とを特徴とする土壌固化剤
4. A soil solidifying agent comprising the soil solidifying agent according to claim 1, further containing 0.3 to 10.0% by weight of a solidifying accelerator.
【請求項5】該固化促進剤は水と反応して炭酸ガスを発
生することが出来る化合物および/または多価金属塩で
ある請求項4に記載の土壌固化剤
5. The soil solidifying agent according to claim 4, wherein the solidification accelerator is a compound capable of reacting with water to generate carbon dioxide gas and / or a polyvalent metal salt.
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