JP2002206090A - Neutral soil-solidifying agent and method of improving ground and the like, and means for preventing elution of heavy metal - Google Patents
Neutral soil-solidifying agent and method of improving ground and the like, and means for preventing elution of heavy metalInfo
- Publication number
- JP2002206090A JP2002206090A JP2001212678A JP2001212678A JP2002206090A JP 2002206090 A JP2002206090 A JP 2002206090A JP 2001212678 A JP2001212678 A JP 2001212678A JP 2001212678 A JP2001212678 A JP 2001212678A JP 2002206090 A JP2002206090 A JP 2002206090A
- Authority
- JP
- Japan
- Prior art keywords
- soil
- solidifying agent
- acidic
- mixed
- magnesium oxide
- 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.)
- Pending
Links
Landscapes
- Consolidation Of Soil By Introduction Of Solidifying Substances Into Soil (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、土壌中性固化剤地
盤等の改良工法及び泥土、ヘドロ改良工法並びに汚染土
壌の重金属等の溶出防止手段の技術分野に関するもので
ある。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the technical field of an improvement method for soil neutral solidifying agent soil and the like, a method for improving mud and sludge, and means for preventing elution of heavy metals and the like from contaminated soil.
【0002】[0002]
【従来の技術】従来の浅層、深層地盤改良工法、泥土、
ヘドロ改良工法等の現場に発生する発生土を固化させる
土壌改良用固化剤としては、セメント系固化剤及び石灰
系固化剤を注入し、混合攪拌して使用していた。2. Description of the Related Art Conventional shallow and deep ground improvement methods, mud,
As a solidifying agent for soil improvement that solidifies generated soil generated on site such as a sludge improvement method, a cement-based solidifying agent and a lime-based solidifying agent were injected, mixed and stirred, and used.
【0003】そのため、上記のような固化剤を使用した
改良固化土は、PH値が、10〜12と高いアルカリ性
の数値を示し、さらに前記セメント系固化剤は、毒性が
強い六価クロムが前記改良固化土に溶け出す恐れがある
と指摘されていた。Therefore, the improved solidified soil using the above-mentioned solidifying agent has a high alkaline value of PH value of 10 to 12, and the cement-based solidifying agent has a highly toxic hexavalent chromium. It was pointed out that there is a risk of melting into the improved solidified soil.
【0004】さらに従来の浅層、深層地盤等の改良工法
においては、ボーリングマシンでボーリングしたり、あ
るいはバックホーで掘り起した後、ソイルセメント又は
セメント系固化剤又は石灰固化剤等の固化剤を注入もし
くは添加し、ロッドの下方に取着する攪拌羽を回転せし
め土壌とよく混合攪拌し、あるいは混合せしめ、固化し
改良土としていた。Further, in a conventional method for improving a shallow or deep ground, a boring machine or a backhoe is used to excavate and then inject a solidifying agent such as a soil cement or a cement solidifying agent or a lime solidifying agent. Alternatively, it was added, and the stirring blade attached to the lower part of the rod was rotated to mix and stir well with the soil, or mixed and solidified to obtain an improved soil.
【0005】そのため、第1に、アルカリ性が著しく高
いことと、第2に前記固化剤の中、特にセメント系固化
剤から毒性が強い六価クロムが溶け出す恐れがあった。[0005] Therefore, first, there is a risk that the alkalinity is extremely high, and secondly, highly toxic hexavalent chromium may be dissolved from the solidifying agent, particularly from the cement-based solidifying agent.
【0006】さらにシールド工事や基礎工事によって発
生する泥土や浚渫工事から発生する高含水率残土のヘド
ロを固化するには、天日乾燥等で長時間を必要とし、且
広大な処理地が必要であった。Further, in order to solidify muddy soil generated by shield work or foundation work or sludge of high water content residual soil generated from dredging work, it takes a long time by drying in the sun, etc., and requires a vast treatment area. there were.
【0007】又前記ヘドロは、脱水機で脱水せしめケー
キ状にしていたので、脱水するのに多くの時間を消費し
ていた。Further, since the sludge is dehydrated by a dehydrator to form a cake, much time is consumed for dehydration.
【0008】さらに従来六価クロム等の重金属によって
汚染されている汚染土壌を浄化する手段としては、当該
個所の土壌を所定の処理場に運搬し、前記土壌中に含有
する汚染物質を除去し、非汚染土壌を投入し埋戻すか、
あるいは前記のように掘り起した汚染土壌を浄化して、
再度前記穴に埋め戻すという浄化手段がなされていた。
そのため浄化処理費用がかさむ等の弊害があった。Further, as means for purifying contaminated soil conventionally contaminated with heavy metals such as hexavalent chromium, the soil at the location is transported to a predetermined treatment plant to remove contaminants contained in the soil. Injecting and backfilling non-contaminated soil,
Or purify the contaminated soil excavated as described above,
Purification means for backfilling the hole again has been used.
For this reason, there have been problems such as an increase in the cost of the purification treatment.
【0009】[0009]
【発明が解決しようとする課題】本発明の土壌中性固化
剤は、毒性の強い六価クロムを含有するセメント系固化
剤の代りに、酸化マグネシウムを主成分とし、さらに処
理土のPH値が5〜9好ましくは5.8〜8.6になる
ように酸性固化助剤を混合した中性固化剤を添加混合せ
しめ、固化強度を著増し、且アルカリ及び重金属汚染の
恐れのない安全な改良土としたものである。The soil neutralizing agent of the present invention contains magnesium oxide as a main component instead of a cement-based solidifying agent containing highly toxic hexavalent chromium, and further has a PH value of the treated soil. 5-9, preferably 5.8-8.6 A neutral solidifying agent mixed with an acidic solidifying aid is added and mixed to increase the solidifying strength remarkably and safely improve without the risk of alkali and heavy metal contamination. It was earth.
【0010】さらに本発明は、浅層、深層地盤改良工事
現場の泥土状等の不良地盤に、前記した酸化マグネシウ
ムを主成分とし、処理土のPH値が5〜9好ましくは
5.8〜8.6になるように酸性固化助剤を混合せしめ
た中性固化剤を使用して、前記と同様な固化強度を著増
し、且アルカリ及び重金属汚染の恐れのない安全な改良
土を得られるようにした。Further, the present invention provides a method for preparing a soil such as a muddy soil in a shallow or deep ground improvement work site, wherein the above-described magnesium oxide is a main component and the PH value of the treated soil is 5-9, preferably 5.8-8. The use of a neutral solidifying agent mixed with an acidic solidifying aid to achieve a solidified strength similar to that described above and a safe improved soil free from alkali and heavy metal contamination. I made it.
【0011】また本発明は、シールド工事や基礎工事現
場に発生する泥土及び浚渫工事から発生ヘドロ内に、土
壌改良剤として、従来の毒性の強い六価クロムを含有す
るセメント系固化剤の代りに、酸化マグネシウムを主成
分とし、処理土のPH値が5〜9好ましくは5.8〜
8.6以内になるように酸性固化助剤を使用して、固化
強度を著増し、且アルカリ及び重金属汚染の恐れのない
安全な改良土を得るようにしたものである。[0011] The present invention also provides a muddy soil generated at a shield work or a foundation work site and a sludge generated from a dredging work, instead of the conventional cement-based solidifying agent containing highly toxic hexavalent chromium as a soil conditioner. , Containing magnesium oxide as a main component, and the pH value of the treated soil is 5 to 9, preferably 5.8 to
The use of an acidic solidification aid so as to be within 8.6 significantly increases the solidification strength and provides a safe improved soil free from alkali and heavy metal contamination.
【0012】さらに本発明は、重金属に汚染されている
汚染土壌において、前記土壌中に含まれている前記重金
属を簡単な手法で、しかも従来の汚染土壌の浄化手段よ
りも、低廉な費用で隣接地の土壌に重金属が再度溶出す
るのを未然に防止せしめることを目的に開発したもので
ある。[0012] Further, the present invention provides a method for contaminating heavy metals contained in contaminated soil in a simple manner and at a lower cost than conventional means for purifying contaminated soil. It was developed to prevent heavy metals from re-eluting into the soil of the ground.
【0013】[0013]
【課題を解決するための手段】請求項1記載の発明は、
酸化マグネシウム100重量部に、10〜100重量%
の酸性固化助剤を混合せしめたことを特徴とする土壌中
性固化剤である。According to the first aspect of the present invention,
10 to 100% by weight based on 100 parts by weight of magnesium oxide
A soil neutral solidifying agent characterized by mixing an acid hardening aid of the above.
【0014】請求項2記載の発明は、前記酸性固化助剤
は、硫酸アルミニウム、ポリ塩化アルミニウム、硫酸第
一鉄、塩化第二鉄、酸性硫酸ナトリウム、スルファミン
酸、リン酸、水溶液のPH値が7以下のリン化合物の
中、単独あるいは二種以上の酸性固化助剤を混合せしめ
たことを特徴とした請求項1記載の土壌中性固化剤であ
る。According to a second aspect of the present invention, the acidic solidification aid has a pH value of aluminum sulfate, polyaluminum chloride, ferrous sulfate, ferric chloride, sodium acid sulfate, sulfamic acid, phosphoric acid, and an aqueous solution. 2. The soil neutral solidifying agent according to claim 1, wherein one or two or more kinds of acidic solidifying aids are mixed among 7 or less phosphorus compounds.
【0015】請求項3記載の発明は、前記固化剤を添加
した改良対象となっている高含水の改良土の場合、前記
固化剤に、吸水剤を併用せしめることを特徴とする請求
項1又は請求項2記載の土壌中性固化剤である。According to a third aspect of the present invention, in the case of a high water content improved soil to which the solidifying agent is added, a water absorbing agent is used in combination with the solidifying agent. The soil neutral solidifying agent according to claim 2.
【0016】請求項4記載の発明は、前記吸水剤は、活
性炭、活性白土、セピオライト、ケイソー土、ゼオライ
ト、シリカヒーム等のポーラスな無機鉱物及びグアガ
ム、硫酸カルシウム、スラグの中、単独又は二種以上混
合して使用するものであることを特徴とする請求項3記
載の土壌中性固化剤である。According to a fourth aspect of the present invention, the water-absorbing agent may be one or more of a porous inorganic mineral such as activated carbon, activated clay, sepiolite, silicate earth, zeolite, and silica heme, and guar gum, calcium sulfate, and slag. The soil neutralizing agent according to claim 3, which is used by mixing.
【0017】請求項5記載の発明は、浅層及び深層の不
良地盤又は軟弱地盤に、請求項1又は2又は3に該当す
る中性固化剤を処理対象土の容量に対し1〜50重量%
添加又は注入し、混合もしくは攪拌せしめて強度が高い
地盤に改良することを特徴とする浅層、深層地盤改良工
法である。According to a fifth aspect of the present invention, the neutral solidifying agent according to the first, second or third aspect is added to the shallow and deep defective ground or soft ground by 1 to 50% by weight based on the volume of the soil to be treated.
This is a method for improving the ground in a shallow or deep layer, characterized in that the ground is improved by adding or pouring, mixing or stirring to improve the ground.
【0018】請求項6記載の発明は、泥土又はヘドロの
内部に、請求項1又は2又は3に該当する中性固化剤を
処理対象土の容量に対し2%〜100重量%添加混合し
改良土として再生し、再生後土地造成土及び道路の路床
土に利用せしめたことを特徴とする泥土、ヘドロ改良工
法である。According to a sixth aspect of the present invention, a neutral solidifying agent according to the first or second or third aspect is added and mixed into mud or sludge by 2% to 100% by weight based on the volume of the soil to be treated. It is a mud and sludge improvement method characterized by reclaiming as soil and using it for land reclamation and road subgrade soil after regeneration.
【0019】請求項7記載の発明は、所定深度の重金属
等によって汚染されている汚染土壌を泥土状となし、前
記泥土状汚染土壌中に、所定の水と所定量の酸化マグネ
シウムを混合した酸化マグネシウムを主成分とする土壌
固化剤を注入して、該固化剤と前記土壌とを混合せし
め、注入した前記固化剤の酸化マグネシウムが反応して
前記土壌を固化して、前記重金属を隣接土壌への溶出を
防止せしめることを特徴とする汚染土壌の重金属等溶出
防止手段である。According to a seventh aspect of the present invention, the contaminated soil contaminated by heavy metal or the like at a predetermined depth is formed into a muddy state, and the muddy contaminated soil is mixed with predetermined water and a predetermined amount of magnesium oxide. A soil solidifying agent containing magnesium as a main component is injected, the solidifying agent is mixed with the soil, the magnesium oxide of the injected solidifying agent reacts to solidify the soil, and the heavy metal is transferred to the adjacent soil. This is a means for preventing elution of heavy metals and the like from contaminated soil, characterized by preventing elution of ash.
【0020】請求項8記載の発明は、前記土壌固化剤
は、前記酸化マグネシウムに対し、水を混合せしめるこ
とを特徴とする請求項7記載の汚染土壌の重金属等溶出
防止手段である。The invention according to claim 8 is the means for preventing elution of heavy metals and the like from contaminated soil according to claim 7, wherein the soil solidifying agent mixes the magnesium oxide with water.
【0021】請求項9記載の発明は、前記土壌固化剤
は、酸化マグネシウム100重量部に、10〜100重
量%の酸性固化助剤を混合せしめたことを特徴とする請
求項7又は同請求項8記載の汚染土壌の重金属等溶出防
止手段である。According to a ninth aspect of the present invention, the soil solidifying agent is obtained by mixing 10 to 100% by weight of an acid solidifying aid with 100 parts by weight of magnesium oxide. 8. Means for preventing elution of heavy metals from contaminated soil according to 8.
【0022】請求項10記載の発明は、前記酸性固化助
剤は、硫酸アルミニウム、ポリ塩化アルミニウム、硫酸
第一鉄、塩化第二鉄、酸性硫酸ナトリウム、スルファミ
ン酸、リン酸、水溶液のPH値が7以下のリン化合物の
中、単独あるいは二種以上の酸性固化助剤を混合せしめ
たことを特徴とした請求項7又は請求項8又は請求項9
記載の汚染土壌の重金属等溶出防止手段である。According to a tenth aspect of the present invention, the acidic solidification aid has a pH value of aluminum sulfate, polyaluminum chloride, ferrous sulfate, ferric chloride, sodium acid sulfate, sulfamic acid, phosphoric acid, and an aqueous solution. 10. The phosphorous compound of 7 or less, wherein one or more kinds of acidic solidification aids are mixed.
Means for preventing elution of heavy metals and the like from the contaminated soil described.
【0023】請求項11記載の発明は、前記土壌固化剤
は、前記重金属の安定化処理のために硫酸第1鉄、又は
塩化第2鉄を添加せしめることを特徴とする請求項7又
は請求項8又は請求項9又は請求項10記載の汚染土壌
の重金属等溶出防止手段である。The invention according to claim 11 is characterized in that the soil solidifying agent adds ferrous sulfate or ferric chloride for stabilizing the heavy metal. A means for preventing elution of heavy metals or the like from contaminated soil according to claim 8 or claim 9 or claim 10.
【0024】請求項12記載の発明は、前記土壌固化剤
は、燐酸化合物、硫酸第一鉄及び塩化第二鉄を単独ある
いは二種以上の酸性固化剤を混合せしめたことを特徴と
する請求項7又は請求項8又は請求項9又は請求項10
又は請求項11記載の汚染土壌の重金属等溶出防止手段
である。According to a twelfth aspect of the present invention, the soil solidifying agent comprises a phosphate compound, ferrous sulfate and ferric chloride alone or as a mixture of two or more acidic solidifying agents. Claim 7 or Claim 8 or Claim 9 or Claim 10
Or a means for preventing elution of heavy metals or the like from contaminated soil according to claim 11.
【0025】請求項13記載の発明は、前記土壌固化剤
は、塩化マグネシウムの酸性固化剤を混合せしめたこと
を特徴とする請求項7又は請求項8又は請求項9又は請
求項10又は請求項11又は請求項12記載の汚染土壌
の重金属等溶出防止手段である。According to a thirteenth aspect of the present invention, the soil hardening agent comprises an acid hardening agent of magnesium chloride mixed therein. A means for preventing elution of heavy metals from contaminated soil according to claim 11 or 12.
【0026】[0026]
【発明の実施の形態】請求項1〜6に記載の発明に関す
る実施の形態は、共通しているので以下のとおり一括し
て説明する。DESCRIPTION OF THE PREFERRED EMBODIMENTS The embodiments according to the first to sixth aspects of the present invention are common and will be described together as follows.
【0027】本発明の中性固化剤は、浅層、深層地盤改
良工事現場の不良地盤を改良するためのものである。The neutral solidifying agent of the present invention is for improving defective ground at a construction site for a shallow or deep ground improvement.
【0028】さらに本発明は、浚渫工事から発生する泥
土及びヘドロを従来の固化方式とは異なり、以下に説明
する固化剤を添加混合し、アルカリ数値が小さく、且重
金属汚染のおそれのない改良土にした。Further, according to the present invention, unlike the conventional solidification method, the mud and sludge generated from the dredging work are mixed with a solidifying agent as described below, and the improved soil having a small alkali value and no risk of heavy metal contamination. I made it.
【0029】本発明の固化剤は、酸化マグネシウム及び
酸化マグネシウムを含有する鉱物100重量部に、10
〜100重量%の酸性固化助剤を混合せしめた土壌中性
固化剤である。The solidifying agent of the present invention contains 10 parts by weight of magnesium oxide and 100 parts by weight of a mineral containing magnesium oxide.
It is a soil neutral solidifying agent mixed with し 100% by weight of an acidic solidifying aid.
【0030】さらに前記酸性固化助剤は、硫酸アルミニ
ウム、ポリ塩化アルミニウム、硫酸第一鉄、塩化第二
鉄、酸性硫酸ナトリウム、スルファミン酸、リン酸、水
溶液のPH値が7以下のリン化合物の中、単独あるいは
二種以上の固化剤を混合せしめたものである。Further, the acidic solidification aid is selected from the group consisting of aluminum sulfate, polyaluminum chloride, ferrous sulfate, ferric chloride, sodium acid sulfate, sulfamic acid, phosphoric acid, and phosphorus compounds having an aqueous solution having a pH of 7 or less. , Or a mixture of two or more solidifying agents.
【0031】また本発明において、対象改良土が高含水
比の場合、前記固化剤に、吸水剤を併用せしめてもよ
い。In the present invention, when the improved soil has a high water content, a water absorbing agent may be used in combination with the solidifying agent.
【0032】前記吸水剤には、活性炭、活性白土、セピ
オライト、ケイソー土、ゼオライト、シリカヒーム等の
ポーラスな無機鉱物及びグアガム、硫酸カルシウム、ス
ラグの中、何れか単独あるいは二種以上混合して使用す
る。As the water-absorbing agent, activated carbon, activated clay, sepiolite, silicate earth, zeolite, porous inorganic minerals such as silica heme, guar gum, calcium sulfate, and slag are used alone or in combination of two or more. .
【0033】さらに本発明は、浅層及び深層の不良地盤
又は軟弱地盤改良工法として、所定の機械等を利用して
ボーリング等を施したボーリング内に前記した酸化マグ
ネシウムを主成分とし、これに酸性固化助剤を混合して
得られた中性固化剤を処理対象土の容量に対し1〜50
重量%添加又は注入し、混合もしくは攪拌せしめ固化す
るものである。その結果下記のとおり強度が高い地盤に
改良することができた。Further, according to the present invention, as a method for improving a shallow or deep defective ground or a soft ground, the above-mentioned magnesium oxide is used as a main component in a boring which has been subjected to boring using a predetermined machine, etc. Neutral solidifying agent obtained by mixing the solidification aid with 1 to 50 to the volume of the soil to be treated.
It is added or injected by weight and mixed or stirred to solidify. As a result, it was possible to improve the ground with high strength as described below.
【0034】[第1実施例]地盤改良処理対象の工事現
場の粗性土の粒径分布が下記のとおりのものにつき、実
施したところつぎのような良好な結果が得られた。[First Embodiment] The following favorable results were obtained when the following improvement was conducted for the following soil coarse particle size distributions at the construction site to be subjected to ground improvement treatment.
【0035】土の粒径分布として、 (1)砂 分 8.4% (2)シルト分 47.6% (3)粘土分 44.0%As the particle size distribution of the soil, (1) sand content 8.4% (2) silt content 47.6% (3) clay content 44.0%
【0036】含土率33.6%、含水率66.4%、含
水比197.6%の高液性シルトの改良対象土1m3当
り50kgの本発明の固化剤をほぼ均一に散布し、これ
をバックホーにて約50cmの深さに掘りかえし混合攪
拌したところ、下記の改良結果が得られた。[0036]含土rate 33.6%, water content 66.4%, substantially uniformly sprayed solidifying agent of the present invention an improved target soil 1 m 3 per 50kg of water content of 197.6% of the high humoral silt, This was dug by a backhoe to a depth of about 50 cm and mixed and stirred, and the following improved results were obtained.
【0037】改良前のコーン指数→0KN/m2 7日後の改良コーン指数→540.5KN/m2 改良土のPH値 8.5Cone index before improvement → 0 KN / m2 Improved cone index after 7 days → 540.5 KN / m2 PH value of improved soil 8.5
【0038】[第2実施例]さらに土の粒径分布とし
て、 (1)砂 分 17.4% (2)シルト分 36.6% (3)粘土分 46.0%[Second Embodiment] Further, the particle size distribution of the soil is as follows: (1) sand content 17.4% (2) silt content 36.6% (3) clay content 46.0%
【0039】含土率37%、含水率63%、含水比17
0.2%の有機質粘土の改良対象土層GL3mから10
mに対し固化剤を改良対象土1m3当り100kgの割
合で注入した。その結果 改良前のコーン指数→0KN/m2 Soil content 37%, water content 63%, water content 17
10% from 3m GL3m for improvement of 0.2% organic clay
To 100 m, a solidifying agent was injected at a rate of 100 kg per 1 m 3 of the soil to be improved. As a result, the cone index before improvement → 0 KN / m 2
【0040】7日後の改良コーン指数→952.1KN
/m2 改良土のPH値 8.6 と良好な改良結果が得られた。Improved cone index after 7 days → 952.1KN
/ M2 The PH value of the improved soil was 8.6, and a good improvement result was obtained.
【0041】[第3実施例]浚渫工事及び泥水シールト
工事から発生したヘドロ又は泥水を、脱水機で脱水する
前工程として、本発明の固化剤を添加し、脱水ケーキを
固化せしめたところ、コーン指数及び好ましいPH値の
改良土がえられた。湖沼ヘドロとして、含水比870%
のヘドロ1m3当りに対し、50kgの固化剤を添加
後、脱水機(フィルタープレス)で脱水したケーキにつ
いて実施したところ、[Third Embodiment] As a pre-process of dehydrating sludge or muddy water generated from dredging work and muddy water seal work with a dewatering machine, the solidifying agent of the present invention was added and the dewatered cake was solidified. An improved soil of index and favorable PH value was obtained. 870% water content as lake sludge
After adding 50 kg of solidifying agent per 1 m 3 of sludge, the cake was dehydrated with a dehydrator (filter press).
【0042】1日後のケーキのコーン指数→1,43
0.1KN/m2 1日後のケーキのPH値 8.7 という好ましい結果が得られた。Cone index of cake after one day → 1,43
0.1KN / m2 A favorable result of PH value of the cake 8.7 after one day was obtained.
【0043】上記の地盤改良工法の実施例を説明する
と、以下のとおりである。An embodiment of the above-mentioned ground improvement method will be described below.
【0044】1は不良地盤、2はバックホー、3は本発
明の固化剤を添加せしめ以下の機械装置によって得られ
た改良土である。Reference numeral 1 denotes defective ground, reference numeral 2 denotes a backhoe, and reference numeral 3 denotes an improved soil obtained by adding the solidifying agent of the present invention and obtaining the following equipment.
【0045】4はボーリングマシン5に装着せしめたロ
ッドである。6は前記ロッド4の頭部に装着した固化剤
注入用スイベルである。7は地盤、8は前記ロッド4の
下方部に取着した攪拌羽である。本発明の固化剤を注入
し混合攪拌すると、攪拌羽8の周辺の不良地盤(泥土
状)が良質の改良土となる。Reference numeral 4 denotes a rod mounted on the boring machine 5. Reference numeral 6 denotes a swivel for injecting a solidifying agent mounted on the head of the rod 4. Reference numeral 7 denotes a ground, and 8 denotes a stirring blade attached to a lower portion of the rod 4. When the solidifying agent of the present invention is injected and mixed and agitated, the defective ground (mud-like) around the agitating blade 8 becomes a high quality improved soil.
【0046】また本発明は、所定の機械等を利用する浚
渫工事によって発生した泥土又はヘドロの内部に、酸化
マグネシウムを主成分とし、このマグネシウムに酸性固
化助剤を混合して得られた中性固化剤を処理対象土の容
量に対し2%〜100%添加し、さらに混合し改良土と
して再生するものである。その結果PH値が9以下で、
且有害金属のない安全な土地造域土として、さらに道路
の路床土として有効に利用できる。Further, according to the present invention, a mud or sludge generated by dredging work using a predetermined machine or the like contains magnesium oxide as a main component, and a neutral solution obtained by mixing the magnesium with an acid-solidifying aid. The solidifying agent is added in an amount of 2% to 100% based on the volume of the soil to be treated, and further mixed to regenerate as an improved soil. As a result, the PH value is 9 or less,
It can be effectively used as a safe land-building soil free of harmful metals and as a roadbed soil.
【0047】図3は本発明の泥土、ヘドロを良質な改良
土に再生する混合装置を図示したものである。FIG. 3 shows a mixing apparatus for regenerating the mud and sludge of the present invention into a high quality improved soil.
【0048】9は混合槽であり、内部には、モーター1
0によって回転するシャフト11の所定個所に羽体12
を取着する。13は泥土投入ホッパー、14は中性固化
剤添加用ホッパーである。Reference numeral 9 denotes a mixing tank in which a motor 1 is provided.
0 at a predetermined position of the shaft 11 which rotates by
Attach. Reference numeral 13 denotes a mud charging hopper, and 14 denotes a hopper for adding a neutral solidifying agent.
【0049】上記装置9に所定量の泥土をホッパー13
より、本発明の中性固化剤を前記ホッパー14より夫々
所定量投入する。羽体12によって混合攪拌され、固化
状態の改良土15となって排出される。A predetermined amount of mud is put into the hopper 13
More specifically, a predetermined amount of the neutral solidifying agent of the present invention is supplied from the hopper 14. The mixture is agitated by the blades 12, and is discharged as solidified improved soil 15.
【0050】16は工事現場において発生した浚渫ヘド
ロ又はシールト泥水の注入径路、17は混合槽、18は
固化剤注入ホッパーである。19は注入した泥水と固化
剤を混合するモーター、20は混合攪拌された泥水の送
水パイプ、21は打込みポンプ、22は送水パイプ、2
3はフィルタープレスである。Reference numeral 16 denotes an injection path of dredged sludge or sealed muddy water generated at the construction site, reference numeral 17 denotes a mixing tank, and reference numeral 18 denotes a solidifying agent injection hopper. 19 is a motor for mixing the injected muddy water and the solidifying agent, 20 is a water pipe for mixing and stirring muddy water, 21 is a driving pump, 22 is a water feeding pipe, 2
3 is a filter press.
【0051】前記フィルタープレス23は、濾布25に
よって構成されている濾室24を内蔵している。The filter press 23 has a built-in filter chamber 24 constituted by a filter cloth 25.
【0052】26は前記フィルタープレス23に接続す
る油圧シリンダーである。27は前記フィルタープレス
23によって脱水された脱水ケーキ、28は前記泥水に
含有されていた濾水である。Reference numeral 26 denotes a hydraulic cylinder connected to the filter press 23. Reference numeral 27 denotes a dewatered cake dewatered by the filter press 23, and reference numeral 28 denotes filtered water contained in the muddy water.
【0053】さらに請求項7〜13に記載の発明に関す
る実施の形態は共通しているので、以下のとおり一括し
て説明する。Further, since the embodiments according to the seventh to thirteenth aspects are common, they will be described collectively as follows.
【0054】本発明の土壌固化剤は、前記1〜6記載の
発明における中性固化剤と同一もしくは類似の成分から
なっている。The soil hardening agent of the present invention comprises the same or similar components as the neutral hardening agent in the above-mentioned inventions 1 to 6.
【0055】本発明は、ボーリングマシンa等を使用し
て、所定深度の重金属等によって汚染されている汚染土
壌を泥土状となし、前記泥土状汚染土壌中に、所定の水
と所定量の酸化マグネシウムを混合した酸化マグネシウ
ムを主成分とする土壌固化剤を注入して、該固化剤と前
記土壌とを混合せしめ、注入した前記固化剤の酸化マグ
ネシウムが反応して前記土壌を固化して、前記重金属を
隣接土壌への溶出を防止せしめるものである。According to the present invention, a polluted soil contaminated by heavy metals or the like at a predetermined depth is made muddy by using a boring machine a or the like, and a predetermined amount of water and a predetermined amount of oxidized water are contained in the muddy contaminated soil. Injecting a soil solidifying agent mainly containing magnesium oxide mixed with magnesium, mixing the solidifying agent and the soil, and reacting the injected magnesium oxide of the solidifying agent to solidify the soil, It prevents heavy metals from eluting into adjacent soil.
【0056】さらに前記土壌固化剤は、前記酸化マグネ
シウムに対し、水を混合せしめたものを使用する。Further, as the soil hardening agent, a mixture of the magnesium oxide and water is used.
【0057】また前記土壌固化剤は、酸化マグネシウム
100重量部に、10〜100重量%の酸性固化助剤を
混合せしめものを使用する。The soil hardening agent is obtained by mixing 10 to 100% by weight of an acid hardening aid with 100 parts by weight of magnesium oxide.
【0058】さらに前記酸性固化助剤は、硫酸アルミニ
ウム、ポリ塩化アルミニウム、硫酸第一鉄、塩化第二
鉄、酸性硫酸ナトリウム、スルファミン酸、リン酸、水
溶液のPH値が7以下のリン化合物の中、単独あるいは
二種以上の酸性固化助剤を混合せしめたものでもよい。Further, the acidic solidification aid includes aluminum sulfate, polyaluminum chloride, ferrous sulfate, ferric chloride, sodium acid sulfate, sulfamic acid, phosphoric acid, and phosphorus compounds having an aqueous solution having a pH value of 7 or less. , Or a mixture of two or more acidic solidification aids.
【0059】また本発明の前記土壌固化剤は、前記重金
属の安定化処理のために硫酸第1鉄、又は塩化第2鉄を
添加せしめてもよい。The soil hardening agent of the present invention may be added with ferrous sulfate or ferric chloride for stabilizing the heavy metal.
【0060】さらに前記土壌固化剤は、燐酸化合物、硫
酸第一鉄及び塩化第二鉄を単独あるいは二種以上の酸性
固化剤を混合せしめたものでもよい。Further, the soil solidifying agent may be a phosphate compound, ferrous sulfate and ferric chloride alone or a mixture of two or more acidic solidifying agents.
【0061】本発明の前記土壌固化剤は、塩化マグネシ
ウムの酸性固化剤を混合せしめたものでもよい。[第1
実施例]The soil hardening agent of the present invention may be a mixture of an acid hardening agent of magnesium chloride. [First
Example]
【0062】所定深度の重金属によって汚染されている
泥土状汚染土壌に本発明の土壌固化剤を混合したとこ
ろ、下記のような良好な結果が得られた。 [測定試験の測定対象の重金属として] (1) 鉛 650mg/kg(この鉛については、環境基準値が0.01mg/l以 下とされている) (2)砒 素 220 〃 ( 〃 0.01 〃 ) (3)セレン 22 〃 ( 〃 0.01 〃 )When the soil solidifying agent of the present invention was mixed with mud-like contaminated soil contaminated with heavy metals at a predetermined depth, the following favorable results were obtained. [As a heavy metal to be measured in the measurement test] (1) Lead 650 mg / kg (for this lead, the environmental standard value is 0.01 mg / l or less) (2) Arsenic 220 〃 (〃 0.01 〃) (3) Selenium 22〃 (〃0.01〃)
【0063】しかるに上記土壌に対し、固化剤(配合比
は下記のとおり。)を混合し、溶出測定試験を行ったと
ころ結果は、下記のとおりであった。When the above soil was mixed with a solidifying agent (compounding ratio is as described below) and an elution measurement test was carried out, the results were as follows.
【0064】固化剤100kg/m3を混入したとこ
ろ、 (1) 鉛 650mg/kg→値が0.005mg/lとなった。 (2)砒 素 220 〃 → 0.005 〃 (3)セレン 22 〃 → 0.005 〃 (4)一軸圧縮強度qu(KN/m2)→7日 21KN/m2 上記のとおり良好な結果が得られた。Solidifying agent 100 kg / m3The place where was mixed
(1) Lead 650 mg / kg → The value became 0.005 mg / l. (2) Arsenic 220 〃 → 0.005 〃 (3) Selenium 22 〃 → 0.005 〃 (4) Uniaxial compressive strength qu (KN / m2) → 21 days 21KN / m2 Good results were obtained as described above.
【0065】さらに固化剤150kg/m3を混合した
ところ、 (1) 鉛 650mg/kg → 値が 0.005mg/l以下となった。 (2)砒 素 220 〃 → 値が 0.005mg/l以下となった。 (3)セレン 22 〃 → 値が 0.005mg/l以下となった。 (4)一軸圧縮強度qu(KN/m2)→7日 22KN/m2 上記のとおり良好な結果が得られた。(第2実施例)Further, when 150 kg / m 3 of the solidifying agent was mixed, (1) lead 650 mg / kg → the value became 0.005 mg / l or less. (2) Arsenic 220 〃 → The value became 0.005 mg / l or less. (3) Selenium 22 〃 → The value became 0.005 mg / l or less. (4) uniaxial compressive strength qu (KN / m 2) → 7 days 22Kn / m 2 above as good results were obtained. (Second embodiment)
【0066】前記第1実施例と相違する所定深度の重金
属によって汚染されている泥土状汚染土壌の含有測定を
行い、さらに固化剤を混合せしめたところ、下記のよう
な良好な結果が得られた。 土壌環境基準 固化剤を混合 固化剤を混合 の値 150kg/m3 200kg/m3 (1)鉛 50mg/kg →0.01mg/l以下 0.005mg/l 0.005 mg/l (2)六価クロム 45mg/kg →0.05mg/l 以下 0.02mg/l 0.01 mg/l 7日 7日 (3)一軸圧縮強度qu(KN/m2) 20KN/m2 22KN/m2 との良い結果が得られた。A heavy metal having a predetermined depth different from that of the first embodiment.
Measurement of mud-like contaminated soil contaminated by genus
Performed and further mixed with a solidifying agent, as shown below
Good results were obtained. Soil environmental standard Mixing of solidifying agent Value of mixing of solidifying agent 150kg / m3 200kg / m3 (1) Lead 50mg / kg → 0.01mg / l or less 0.005mg / l 0.005mg / l (2) Hexavalent chromium 45mg / kg → 0.05mg / l or less 0.02mg / l 0.01mg / l 7 days 7 days (3 ) Uniaxial compressive strength qu (KN / m2) 20KN / m2 22KN / m2 With good results.
【0067】上記のように混合した固化剤は以下のとお
りであった。 酸化マグネシウム 50% 過リン酸石灰 25% 硫酸第一鉄 25%The solidifying agents mixed as described above were as follows. Magnesium oxide 50% Lime perphosphate 25% Ferrous sulfate 25%
【0068】aはロッドbを汚染土壌cの地中に進入さ
せるボーリングマシンである。このマシンaは従来から
使用されているものである。Reference numeral a denotes a boring machine for moving the rod b into the contaminated soil c. This machine a has been used in the past.
【0069】ロッドbの構造も、従来公知のものを使用
する。その具体的構成は以下のとおりである。As the structure of the rod b, a conventionally known structure is used. The specific configuration is as follows.
【0070】30は超高圧水を噴射せしめる上段に送り
込み口部31を設けた通水部、32は前記通水部30の
下段に設けた圧縮空気の送り込み口部であり、前記通水
部30と連通する。Reference numeral 30 denotes a water passage provided with an inlet 31 at an upper stage for injecting ultra-high pressure water, and 32 denotes a compressed air inlet provided at a lower stage of the water passage 30. Communicate with
【0071】本発明の土壌固化剤を注入する手段は、従
来の注入法と同じである。The means for injecting the soil hardening agent of the present invention is the same as the conventional injection method.
【0072】前記請求項7〜13記載の発明の要旨は、
第1に、検知テストの結果、重金属が存在する地層より
若干下方の地層に、前記した構造のロッドbを進入させ
る。第2に前記のように進入したロッドbより、超高圧
水と、圧縮空気を噴射させながら、前記ロッドbを所定
のスピードで回転させる。第3に前記ロッドbを、ノズ
ルから超高圧水を、エアーをエアノズルから噴射させ、
回転させながら、所定の高さまで引揚げる。The gist of the invention described in claims 7 to 13 is that
First, as a result of the detection test, the rod b having the above-described structure is caused to enter a formation slightly below a formation in which heavy metal exists. Secondly, the rod b is rotated at a predetermined speed while injecting ultra-high pressure water and compressed air from the rod b that has entered as described above. Third, the rod b is sprayed with ultra-high pressure water from a nozzle and air from an air nozzle,
While rotating, pull up to a predetermined height.
【0073】上記のようにロッドbを下方から上方へと
移動することによって、汚染土壌c及びその周辺の土壌
が円筒状にして、且泥土状となっている。By moving the rod b upward from below as described above, the contaminated soil c and the surrounding soil are cylindrical and muddy.
【0074】従来の技法では、上記のように泥土状とな
った汚染土壌cは、吸上げられスライムピットに貯蔵後
所定の処理場に搬送され、適宜処理されている。In the conventional technique, the contaminated soil c, which has become muddy as described above, is sucked up, stored in a slime pit, transported to a predetermined treatment plant, and appropriately treated.
【0075】上記のように円筒状にして、且泥土状とな
っている汚染土壌cに対し、前記ロッドbの固化剤噴射
ノズルから、以下に説明する本発明の要旨である所定量
の固化剤を前記ロッドbを回転させながら注入し、泥土
状の汚染土壌cと混合攪拌する。The contaminated soil c, which is cylindrical and muddy as described above, is injected from the solidifying agent injection nozzle of the rod b with a predetermined amount of solidifying agent, which is the subject of the present invention described below. Is injected while rotating the rod b, and mixed and stirred with the mud-like contaminated soil c.
【0076】しかる後、前記ロッドbを引揚げ、所定時
間後、前記固化剤の吸水特性を利用して、前記泥土状の
汚染土壌cを約7時間で固化せしめる。その結果有害物
質の重金属は、安定化して他の周辺土壌への溶出が防止
される。Thereafter, the rod b is pulled up, and after a predetermined time, the mud-like contaminated soil c is solidified in about 7 hours by using the water absorbing property of the solidifying agent. As a result, the heavy metals of the harmful substances are stabilized and are prevented from being eluted into other surrounding soils.
【0077】つぎに本発明の固化剤を説明する。Next, the solidifying agent of the present invention will be described.
【0078】酸化マグネシウムを主成分とする固化剤
は、注入前予め水によって溶解しておく。The solidifying agent mainly composed of magnesium oxide is dissolved in water before injection.
【0079】上記のように溶解した前記酸化マグネシウ
ムを、ノズルから噴射する。前記酸化マグネシウムは、
泥土状となっている汚染土壌中に含有する水を吸収し、
所定時間(8〜10時間)後、泥土状となっていた汚染
土壌を固化せしめる。The magnesium oxide dissolved as described above is jetted from a nozzle. The magnesium oxide is
Absorbs water contained in muddy contaminated soil,
After a predetermined time (8 to 10 hours), the contaminated soil that has been muddy is solidified.
【0080】前記のように、固化した汚染土壌に含有す
る六価クロム又はトリクロロエチレン等の重金属は、長
期間安定化し、周辺土壌に溶出しない。As described above, heavy metals such as hexavalent chromium or trichlorethylene contained in solidified contaminated soil are stabilized for a long period of time and do not elute into the surrounding soil.
【0081】さらに本発明の固化剤である他の実施例の
場合でも、泥土状の汚染土壌は、所定時間後固化し、前
記重金属は安定して周辺土壌には溶出しない。Further, even in the case of the other embodiment which is the solidifying agent of the present invention, the mud-like contaminated soil solidifies after a predetermined time, and the heavy metal does not stably elute into the surrounding soil.
【0082】さらに本発明は、六価クロム又はトリクロ
ロエチレンの重金属によって汚染されている所定深度の
汚染土壌の地中に、ボーリングマシンを介して超高圧水
の通水部、圧縮空気の送り込み部及び固化剤の通水部を
有するロッドを所定の深さまで進入せしめ、進入後前記
ロッドを構成する超高圧水の通水部より、超高圧水を噴
射せしめ、所定の幅員と所定の高さの前記汚染土壌を噴
射水によって泥土状とし、さらに所定の水に所定量の酸
化マグネシウムを主成分とする土壌固化剤を、前記ロッ
ドの固化剤通水部を介して、前記ロッドを回転せしめな
がら固化剤ノズルより噴射して、前記泥土状の土壌中に
混合攪拌せしめ、前記固化剤の特性である吸着性を利用
して前記泥土状の土壌を強固に固化せしめ、前記重金属
物質の再溶出を防止せしめる工法もできる。Further, the present invention provides a process for passing a super high pressure water through a boring machine, feeding a compressed air, and solidifying into a soil of a contaminated soil at a predetermined depth which is contaminated by a heavy metal of hexavalent chromium or trichlorethylene. The rod having the water passage of the agent is made to enter a predetermined depth, and after the penetration, the ultra-high pressure water is injected from the water passage of the ultra-high pressure water constituting the rod, and the contamination of a predetermined width and a predetermined height is performed. The soil is made muddy by spraying water, and a soil solidifying agent containing a predetermined amount of magnesium oxide as a main component in predetermined water is passed through the solidifying water passage section of the rod while the rod is rotated while the solidifying agent nozzle is rotated. The muddy soil is mixed and stirred into the muddy soil, and the muddy soil is solidified firmly by using the adsorptive property of the solidifying agent to prevent re-elution of the heavy metal substance. Allowed to method can also be.
【0083】[0083]
【発明の効果】請求項1記載の発明は、酸化マグネシウ
ム及び酸化マグネシウムを含有する鉱物100重量部
に、10〜100重量%の酸性固化助剤を混合せしめた
土壌中性固化剤なので、前記酸化マグネシウムと酸性固
化助剤が不良地盤や軟弱地盤等の土壌内に注入されると
前記土壌中に含有する水分と結合して固化せしめ、前記
不良地盤や軟弱地盤を強度の大きい良好な地盤にするこ
とができた。According to the first aspect of the present invention, there is provided a soil neutral solidifying agent obtained by mixing 10 to 100% by weight of an acidic solidifying aid with 100 parts by weight of magnesium oxide and a mineral containing magnesium oxide. When magnesium and acidic solidification aids are injected into soil such as defective ground or soft ground, they combine with the water contained in the soil and solidify, thereby turning the defective ground or soft ground into a strong ground with good strength. I was able to.
【0084】さらに本発明の中性固化剤の使用によっ
て、改良された固化土は、PH値が5〜9好ましくは
5.8〜8.6以内なので、有害金属とされている六価
クロム等は含有しない重金属汚染のおそれのない安全な
改良土が得られる利点がある。The solidified soil improved by the use of the neutral solidifying agent of the present invention has a PH value of 5 to 9, preferably 5.8 to 8.6. There is an advantage that a safe improved soil free of heavy metal contamination which does not contain is obtained.
【0085】請求項2記載の発明の前記酸性固化助剤
は、硫酸アルミニウム、ポリ塩化アルミニウム、硫酸第
一鉄、塩化第二鉄、酸化硫酸ナトリウム、スルファミン
酸、リン酸、水溶液のPH値が7以下のリン化合物の
中、単独あるいは二種以上の固化剤を混合せしめた土壌
中性固化剤なので、前記酸性固化助剤の単独あるいは2
種以上の固化剤を含む中性固化剤を前記請求項1と同じ
不良地盤や軟弱地盤等の土壌内に注入すると、前記酸化
マグネシウムと前記酸性固化助剤が、前記土壌中に含有
する水分と結合して固化し、強度の大きい良好な地盤を
形成することができた。The acid hardening aid according to the second aspect of the present invention includes aluminum sulfate, polyaluminum chloride, ferrous sulfate, ferric chloride, sodium oxide, sulfamic acid, phosphoric acid, and an aqueous solution having a pH value of 7%. Among the following phosphorus compounds, a single or a mixture of two or more solidifying agents is a soil neutral solidifying agent.
When a neutral solidifying agent containing at least one kind of solidifying agent is injected into soil such as the same defective ground or soft ground as in claim 1, the magnesium oxide and the acidic solidification aid are mixed with water contained in the soil. It was bonded and solidified, and a good ground with high strength could be formed.
【0086】さらに本発明の中性固化剤の使用によっ
て、改良された固化土は、PH値が5〜9好ましくは
5.8〜8.6以内なので、有害金属とされている六価
クロム等は含有しない重金属汚染のおそれのない安全な
改良土が得られる利点がある。Further, the solidified soil improved by the use of the neutral solidifying agent of the present invention has a PH value of 5 to 9, preferably 5.8 to 8.6. There is an advantage that a safe improved soil free of heavy metal contamination which does not contain is obtained.
【0087】請求項3記載の発明は、前記固化剤に、吸
水剤を併用せしめた土壌中性固化剤なので、高含水の前
記不良地盤や軟弱地盤等の土壌内に注入されると、含水
比が高くても十分固化し、固さも十分に固い改良地盤等
を得ることができた。The third aspect of the present invention is a soil-neutral solidifying agent in which a water-absorbing agent is used in combination with the solidifying agent. However, the improved ground and the like which were sufficiently hardened even when the hardness was high and the hardness was sufficiently hard could be obtained.
【0088】請求項4記載の発明は、前記吸水剤が、活
性炭、活性白土、セピオライト、ケイソー土、ゼオライ
ト、シリカヒーム等のポーラスな無機鉱物及びグアガ
ム、硫酸カルシウム、スラグの中、単独又は二種以上混
合して使用するものである土壌中性固化剤なので、前記
吸水剤を使用することによって、前記請求項3と同じ効
果を得ることができた。The invention according to claim 4 is characterized in that the water-absorbing agent is one or more of porous inorganic minerals such as activated carbon, activated clay, sepiolite, kieselguhr, zeolite, silica heme and guar gum, calcium sulfate and slag. Since it is a soil-neutral solidifying agent to be used by mixing, the same effect as in claim 3 can be obtained by using the water-absorbing agent.
【0089】請求項5記載の発明は、浅層及び深層の不
良地盤又は軟弱地盤に、酸化マグネシウムを主成分と
し、前記酸化マグネシウムに酸性固化剤を混合した中性
固化剤を処理対象土の容量に対し1〜50重量%添加又
は注入し、混合もしくは攪拌せしめた浅層、深層地盤改
良工法なので、前記中性固化剤が注入されると、前記浅
層及び深層の不良地盤又は軟弱地盤の水分と結合固化
し、固化強度を著増し、さらにアルカリ及び重金属汚染
のおそれのない安全な改良土を極めて容易に得られる利
点がある。According to a fifth aspect of the present invention, a neutral solidifying agent containing magnesium oxide as a main component and an acidic solidifying agent mixed with the magnesium oxide is applied to the shallow and deep defective ground or soft ground. 1 to 50% by weight, or mixed and agitated, is mixed or agitated. Therefore, when the neutral solidifying agent is injected, moisture in the shallow and deep defective ground or soft ground is added. The solidification is significantly increased, and furthermore, there is an advantage that a safe improved soil free from the possibility of alkali and heavy metal contamination can be obtained very easily.
【0090】請求項6記載の発明は、泥土又はヘドロの
内部に、酸化マグネシウムを主成分とし、前記酸化マグ
ネシウムに酸性固化助剤を混合した中性固化剤を処理対
象土の容量に対し2%〜100重量%添加混合し改良土
として再成する泥土、ヘドロ改良工法なので、従来の泥
土、ヘドロ改良工法と異なり、固化強度を著増し、且ア
ルカリ及び重金属汚染のおそれのない安全な土地造成土
あるいは道路の路床土を確実に得ることができる。According to a sixth aspect of the present invention, in the mud or sludge, a neutral solidifying agent containing magnesium oxide as a main component and an acidic solidifying aid mixed with the magnesium oxide is used in an amount of 2% based on the volume of the soil to be treated. Up to 100% by weight is added and mixed to regenerate as improved soil. Since it is a sludge improvement method, unlike the conventional mud and sludge improvement method, the solidification strength is significantly increased and there is no risk of alkali and heavy metal contamination. Alternatively, it is possible to reliably obtain the subgrade soil of the road.
【0091】請求項7記載の発明は、所定深度の重金属
等によって汚染されている汚染土壌を泥土状となし、前
記泥土状汚染土壌中に、所定の水と所定量の酸化マグネ
シウムを混合した酸化マグネシウムを主成分とする土壌
固化剤を注入して、該固化剤と前記土壌とを混合せし
め、注入した前記固化剤の酸化マグネシウムが反応して
前記土壌を固化して、前記重金属を隣接土壌への溶出を
防止せしめる汚染土壌の重金属等溶出防止手段なので、
注入した酸化マグネシウムが、泥土状態となっている含
有水分を吸収せしめると共に、泥土状態となっている前
記土壌を強固に固化して、有害の重金属を安定化し、再
度溶出するのを確実に防止せしめた。According to a seventh aspect of the present invention, the contaminated soil contaminated by heavy metal or the like at a predetermined depth is formed into a mud-like state, and a predetermined amount of water and a predetermined amount of magnesium oxide are mixed in the mud-like contaminated soil. A soil solidifying agent containing magnesium as a main component is injected, the solidifying agent is mixed with the soil, the magnesium oxide of the injected solidifying agent reacts to solidify the soil, and the heavy metal is transferred to the adjacent soil. It is a means of preventing elution of heavy metals from contaminated soil that prevents elution of
The injected magnesium oxide absorbs the water contained in the mud state and firmly solidifies the soil in the mud state, stabilizes harmful heavy metals and reliably prevents elution again. Was.
【0092】さらに本発明は、従来の汚染土壌の浄化手
段の一つであった、いわゆる汚染土壌をそのまま掘り起
し、掘り起した土壌を他の処理場に運搬し、所定の浄化
処理を行ったり、あるいは掘り起された凹地に、重金属
に汚染されていない土壌を投入する入替え手段がなされ
ていたものと異なり、重金属による汚染土壌とその周辺
の土壌を超高圧水を噴射して円筒状に泥土化し、前記泥
土化した土壌の水分を前記本発明の固化である酸化マグ
ネシウムを介して吸収し、且前記マグネシウムの特性で
ある固化機能によって前記土壌を強固に固化せしめ、重
金属の再度の溶出を防止する手段としたので、汚染土壌
内の重金属の封鎖を従来の硬化手段よりも低廉な費用で
処理できる利点がある。Further, the present invention excavates so-called contaminated soil as one of the conventional means for purifying contaminated soil, transports the excavated soil to another treatment plant, and performs a predetermined purification treatment. In contrast to those in which replacement means for introducing soil not contaminated with heavy metal into the excavated or excavated concavities were used, the soil contaminated by heavy metal and the surrounding soil were sprayed with ultra-high pressure water to form a cylinder. The muddy soil absorbs the water of the muddy soil through the solidified magnesium oxide of the present invention, and solidifies the soil firmly by the solidification function which is a characteristic of the magnesium, thereby preventing the elution of heavy metals again. The prevention means has the advantage that the sequestration of heavy metals in the contaminated soil can be treated at a lower cost than conventional hardening means.
【0093】請求項8記載の発明は、前記土壌固化剤
は、前記酸化マグネシウムに対し、水を混合せしめるた
汚染土壌の重金属等溶出防止手段なので、前記請求項7
記載の発明と同様の効果を有している。According to the present invention, the soil solidifying agent is a means for preventing water from being mixed with the magnesium oxide to prevent elution of heavy metals and the like in contaminated soil.
It has the same effect as the described invention.
【0094】請求項9記載の発明は、前記土壌固化剤
は、酸化マグネシウム100重量部に、10〜100重
量%の酸性固化助剤を混合せしめた汚染土壌の重金属等
溶出防止手段なので、汚染土壌の固化を、より一層強固
に固化せしめることができる。According to a ninth aspect of the present invention, the soil solidifying agent is a means for preventing elution of heavy metals and the like in contaminated soil obtained by mixing 10 to 100% by weight of an acid solidifying aid with 100 parts by weight of magnesium oxide. Can be further solidified.
【0095】請求項10記載の発明は、前記酸性固化助
剤は、硫酸アルミニウム、ポリ塩化アルミニウム、硫酸
第一鉄、塩化第二鉄、酸性硫酸ナトリウム、スルファミ
ン酸、リン酸、水溶液のPH値が7以下のリン化合物の
中、単独あるいは二種以上の酸性固化助剤を混合せしめ
た汚染土壌の重金属等溶出防止手段なので、前記請求項
7〜9記載の発明と同じ効果を有している。The invention according to claim 10 is characterized in that the acidic solidification aid has a pH value of aluminum sulfate, polyaluminum chloride, ferrous sulfate, ferric chloride, sodium acid sulfate, sulfamic acid, phosphoric acid, and an aqueous solution. It is the means for preventing elution of heavy metals and the like from contaminated soil in which a single or two or more acidic solidification assistants are mixed among the phosphorus compounds of 7 or less.
【0096】請求項11記載の発明は、前記土壌固化剤
は、前記重金属の安定化処理のために硫酸第1鉄、又は
塩化第2鉄を添加せしめた汚染土壌の重金属等溶出防止
手段なので、請求項7〜10記載の発明と同じ効果を有
する。The invention according to claim 11 is that the soil solidifying agent is a means for preventing elution of heavy metals and the like in contaminated soil to which ferrous sulfate or ferric chloride is added for stabilizing the heavy metals. It has the same effect as the invention according to claims 7 to 10.
【0097】請求項12記載の発明は、前記土壌固化剤
は、燐酸化合物、硫酸第一鉄及び塩化第二鉄を単独ある
いは二種以上の酸性固化剤を混合せした汚染土壌の重金
属等溶出防止手段なので、請求項7〜11記載の発明と
同じ効果を有する。According to a twelfth aspect of the present invention, the soil solidifying agent is a phosphate compound, ferrous sulfate and ferric chloride used alone or as a mixture of two or more acidic solidifying agents to prevent elution of heavy metals and the like from contaminated soil. Since it is a means, it has the same effect as the inventions of claims 7 to 11.
【0098】請求項13記載の発明は、前記土壌固化剤
は、塩化マグネシウムの酸性固化剤を混合せしめた汚染
土壌の重金属等溶出防止手段なので、請求項7〜12記
載の発明と同じ効果を有する。According to a thirteenth aspect of the present invention, the soil solidifying agent is a means for preventing elution of heavy metals and the like in contaminated soil mixed with an acidic solidifying agent of magnesium chloride, and thus has the same effect as the inventions of the seventh to twelfth aspects. .
【図1】本発明の土壌中性固化剤及び地盤等の改良工法
における浅層不良地盤等改良工法における浅層不良地盤
の改良作業状態を示す図である。BRIEF DESCRIPTION OF DRAWINGS FIG. 1 is a diagram showing a state of work for improving a shallow-layer defective ground in a method for improving a shallow-layer defective ground in a method for improving a soil-neutral solidifying agent and ground according to the present invention.
【図2】深層地盤改良時の作業状態を示す図である。FIG. 2 is a diagram showing a working state at the time of deep ground improvement.
【図3】混合槽内に泥土に固化剤を投入し、混合攪拌し
て改良土を製造せしめた機構を示す図である。FIG. 3 is a view showing a mechanism in which a solidifying agent is put into mud in a mixing tank and mixed and stirred to produce an improved soil.
【図4】第2実施例のヘドロ等を脱水ケーキと濾水に脱
水分離せしめるフィルタープレスの系統図である。FIG. 4 is a system diagram of a filter press according to a second embodiment for separating sludge and the like into a dewatered cake and drainage.
【図5】本発明の汚染土壌の重金属等溶出防止手段の一
部切欠縦断面図である。FIG. 5 is a partially cutaway longitudinal sectional view of a means for preventing elution of heavy metals or the like from contaminated soil according to the present invention.
【図6】図5の防止手段において使用するロッドの一部
切欠拡大縦断面図である。FIG. 6 is a partially cut-away enlarged longitudinal sectional view of a rod used in the prevention means of FIG. 5;
a ボーリングマシン b ロッド c 汚染土壌 1 不良地盤 2 バックホー 3 改良土 4 ロッド 5 ボーリングマシン 6 スイベル 7 地盤 8 攪拌羽 9 混合槽 10 モーター 11 シャフト 12 羽体 13、14 ホッパー 15 改良土 16 送泥管 17 混合槽 18 注入ホッパー 19 攪拌モーター 20 送泥管 21 打込みポンプ 22 送泥管 23 フィルタープレス 24 濾室 25 濾布 26 油圧シリンダー 27 脱水ケーキ 28 濾水 a boring machine b rod c contaminated soil 1 defective ground 2 backhoe 3 improved soil 4 rod 5 boring machine 6 swivel 7 ground 8 stirring blade 9 mixing tank 10 motor 11 shaft 12 blade 13 and 14 hopper 15 improved soil 16 mud pipe 17 Mixing tank 18 Injection hopper 19 Stirring motor 20 Mud feed pipe 21 Driving pump 22 Mud feed pipe 23 Filter press 24 Filter chamber 25 Filter cloth 26 Hydraulic cylinder 27 Dehydration cake 28 Drainage
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) E02D 3/12 101 E02D 3/12 102 102 C09K 103:00 // C09K 103:00 109:00 109:00 B09B 3/00 ZAB Fターム(参考) 2D040 AA01 AB01 AB03 AC05 CA08 4D004 AA41 AB03 AC07 CA15 CB27 CC03 CC11 DA03 DA10 4D059 AA09 BF16 BG00 BG03 BJ01 CC04 DA01 DA06 DA08 DA09 DA16 DA17 DA23 DA24 DA31 DA39 DA54 DA55 DA61 DA70 4H026 CA04 CA06 CB01 CB03 CB05 CB07 CC02 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) E02D 3/12 101 E02D 3/12 102 102 C09K 103: 00 // C09K 103: 00 109: 00 109: 00 B09B 3/00 ZAB F term (reference) 2D040 AA01 AB01 AB03 AC05 CA08 4D004 AA41 AB03 AC07 CA15 CB27 CC03 CC11 DA03 DA10 4D059 AA09 BF16 BG00 BG03 BJ01 CC04 DA01 DA06 DA08 DA09 DA16 DA17 DA40 DA54 DA06 DA54 CB01 CB03 CB05 CB07 CC02
Claims (13)
100重量%の酸性固化助剤を混合せしめたことを特徴
とする土壌中性固化剤。(1) 100 parts by weight of magnesium oxide, 10 to 10 parts by weight
A soil-neutral solidifying agent comprising 100% by weight of an acidic solidifying aid.
ポリ塩化アルミニウム、硫酸第一鉄、塩化第二鉄、酸性
硫酸ナトリウム、スルファミン酸、リン酸、水溶液のP
H値が7以下のリン化合物の中、単独あるいは二種以上
の酸性固化助剤を混合せしめたことを特徴とした請求項
1記載の土壌中性固化剤。2. The method according to claim 1, wherein the acidic solidification aid is aluminum sulfate,
Polyaluminum chloride, ferrous sulfate, ferric chloride, sodium acid sulfate, sulfamic acid, phosphoric acid, P of aqueous solution
2. The soil neutral solidifying agent according to claim 1, wherein a single or two or more kinds of acidic solidifying aids are mixed among phosphorus compounds having an H value of 7 or less.
る高含水比の改良土の場合、前記固化剤に、吸水剤を併
用せしめることを特徴とする請求項1又は請求項2記載
の土壌中性固化剤。3. The improvement soil according to claim 1, wherein a water absorbing agent is used in combination with the solidification agent in the case of an improved soil having a high water content to which the solidification agent is added. Soil neutral solidifying agent.
ライト、ケイソー土、ゼオライト、シリカヒーム等のポ
ーラスな無機鉱物及びグアガム、硫酸カルシウム、スラ
グの中、単独又は二種以上混合して使用するものである
ことを特徴とする請求項3記載の土壌中性固化剤。4. The water-absorbing agent is used alone or as a mixture of two or more of activated carbon, activated clay, sepiolite, silicate earth, zeolite, and porous inorganic minerals such as silica fume and guar gum, calcium sulfate, and slag. The soil neutral solidifying agent according to claim 3, wherein
請求項1又は2又は3に該当する中性固化剤を処理対象
土の容量に対し1〜50重量%添加又は注入し、混合も
しくは攪拌せしめて強度が高い地盤に改良することを特
徴とする浅層、深層地盤改良工法。5. In shallow and deep defective ground or soft ground,
A shallow ground characterized by adding or injecting 1 to 50% by weight of the neutral solidifying agent corresponding to claim 1, 2 or 3 with respect to the volume of the soil to be treated and mixing or stirring to improve the ground with high strength. Layer, deep ground improvement method.
又は3に該当する中性固化剤を処理対象土の容量に対し
2%〜100重量%添加混合し改良土として再生し、再
生後土地造成土及び道路の路床土に利用せしめたことを
特徴とする泥土、ヘドロ改良工法。6. The method according to claim 1, wherein the inside of the mud or the sludge is embedded in the sludge.
Alternatively, 2% to 100% by weight of a neutral solidifying agent corresponding to 3 is added to and mixed with the volume of the soil to be treated, and the mixed soil is regenerated as an improved soil. Mud and sludge improvement method.
る汚染土壌を泥土状となし、前記泥土状汚染土壌中に、
所定の水と所定量の酸化マグネシウムを混合した酸化マ
グネシウムを主成分とする土壌固化剤を注入して、該固
化剤と前記土壌とを混合せしめ、注入した前記固化剤の
酸化マグネシウムが反応して前記土壌を固化して、前記
重金属を隣接土壌への溶出を防止せしめることを特徴と
する汚染土壌の重金属等溶出防止手段。7. A muddy contaminated soil contaminated with heavy metal or the like at a predetermined depth, wherein said muddy contaminated soil includes:
A soil solidifying agent containing magnesium oxide as a main component, in which predetermined water and a predetermined amount of magnesium oxide are mixed, is injected, and the solidifying agent and the soil are mixed, and the injected magnesium oxide of the solidifying agent reacts. A means for preventing the elution of heavy metals or the like from contaminated soil, wherein the soil is solidified to prevent the heavy metals from being eluted into adjacent soil.
に対し、水を混合せしめることを特徴とする請求項7記
載の汚染土壌の重金属等溶出防止手段。8. The means for preventing elution of contaminated soil such as heavy metals according to claim 7, wherein said soil solidifying agent mixes said magnesium oxide with water.
0重量部に、10〜100重量%の酸性固化助剤を混合
せしめたことを特徴とする請求項7又は同請求項8記載
の汚染土壌の重金属等溶出防止手段。9. The method according to claim 9, wherein the soil solidifying agent is magnesium oxide 10
9. The means for preventing elution of heavy metals or the like from contaminated soil according to claim 7 or 8, wherein 10 to 100% by weight of an acidic solidification aid is mixed with 0 parts by weight.
ム、ポリ塩化アルミニウム、硫酸第一鉄、塩化第二鉄、
酸性硫酸ナトリウム、スルファミン酸、リン酸、水溶液
のPH値が7以下のリン化合物の中、単独あるいは二種
以上の酸性固化助剤を混合せしめたことを特徴とした請
求項7又は請求項8又は請求項9記載の汚染土壌の重金
属等溶出防止手段。10. The method according to claim 1, wherein the acid hardening aid is aluminum sulfate, polyaluminum chloride, ferrous sulfate, ferric chloride,
9. A method according to claim 7, wherein a single or two or more kinds of acidic solidification aids are mixed among the acidic sodium sulfate, sulfamic acid, phosphoric acid and a phosphorus compound having an aqueous solution having a pH value of 7 or less. The means for preventing elution of heavy metals or the like from contaminated soil according to claim 9.
処理のために硫酸第1鉄、又は塩化第2鉄を添加せしめ
ることを特徴とする請求項7又は請求項8又は請求項9
又は請求項10記載の汚染土壌の重金属等溶出防止手
段。11. The soil solidifying agent according to claim 7, wherein ferrous sulfate or ferric chloride is added for stabilizing the heavy metal.
Or means for preventing elution of heavy metals or the like from contaminated soil according to claim 10.
一鉄及び塩化第二鉄を単独あるいは二種以上の酸性固化
剤を混合せしめたことを特徴とする請求項7又は請求項
8又は請求項9又は請求項10又は請求項11記載の汚
染土壌の重金属等溶出防止手段。12. The soil solidifying agent according to claim 7, wherein a phosphate compound, ferrous sulfate and ferric chloride are used alone or in combination of two or more acidic solidifying agents. The means for preventing elution of heavy metals or the like from contaminated soil according to claim 9 or claim 10.
酸性固化剤を混合せしめたことを特徴とする請求項7又
は請求項8又は請求項9又は請求項10又は請求項11
又は請求項12記載の汚染土壌の重金属等溶出防止手
段。13. The soil hardening agent according to claim 7, wherein an acid hardening agent of magnesium chloride is mixed.
13. The means for preventing elution of heavy metals or the like from contaminated soil according to claim 12.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2001212678A JP2002206090A (en) | 2000-11-09 | 2001-07-12 | Neutral soil-solidifying agent and method of improving ground and the like, and means for preventing elution of heavy metal |
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000-341742 | 2000-11-09 | ||
JP2000341742 | 2000-11-09 | ||
JP2001212678A JP2002206090A (en) | 2000-11-09 | 2001-07-12 | Neutral soil-solidifying agent and method of improving ground and the like, and means for preventing elution of heavy metal |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2002206090A true JP2002206090A (en) | 2002-07-26 |
Family
ID=26603645
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2001212678A Pending JP2002206090A (en) | 2000-11-09 | 2001-07-12 | Neutral soil-solidifying agent and method of improving ground and the like, and means for preventing elution of heavy metal |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2002206090A (en) |
Cited By (29)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002167582A (en) * | 2000-11-29 | 2002-06-11 | Matsuda Giken Kogyo Kk | Soil stabilizer |
JP2003117532A (en) * | 2001-10-09 | 2003-04-22 | Taiheiyo Cement Corp | Solidifying material and solidifying method for suppressing elution of heavy metal |
JP2003334526A (en) * | 2002-05-21 | 2003-11-25 | Konoike Constr Ltd | Method for solidifying and insolubilizing polluted soil, or the like |
JP2004131550A (en) * | 2002-10-09 | 2004-04-30 | Mitsubishi Materials Corp | Method for producing granulated soil |
JP2004203962A (en) * | 2002-12-24 | 2004-07-22 | Kurita Water Ind Ltd | Mud-solidifying agent and solidifying method |
JP2004292568A (en) * | 2003-03-26 | 2004-10-21 | Taiheiyo Cement Corp | Soil solidifying material |
JP2005002190A (en) * | 2003-06-11 | 2005-01-06 | Mirai Kensetsu Kogyo Kk | Soil improving material safe for marine organism and method for evaluating safety thereof |
JP2005007256A (en) * | 2003-06-18 | 2005-01-13 | Matsuda Giken Kogyo Kk | Contaminated soil insolubilization solidification agent |
JP2005028343A (en) * | 2003-07-11 | 2005-02-03 | Takenaka Komuten Co Ltd | Method for preventing elution of harmful metal from harmful metal contaminated waste product |
JP2005113065A (en) * | 2003-10-10 | 2005-04-28 | Kajima Corp | Consolidating agent for ground improvement and ground improvement method of construction |
JP2006000692A (en) * | 2004-06-15 | 2006-01-05 | Konoike Constr Ltd | Treatment method for dehydrating/hardening dredged soil or the like |
JP2006026472A (en) * | 2004-07-13 | 2006-02-02 | Asahi Kagaku Kogyo Co Ltd | Method for neutralizing alkali soil and leachate from the soil |
JPWO2004078374A1 (en) * | 2003-03-03 | 2006-06-08 | 日本板硝子株式会社 | Soil conditioner |
JP2006219547A (en) * | 2005-02-09 | 2006-08-24 | Matsuda Giken Kogyo Kk | Soil-solidifying material |
JP2007268382A (en) * | 2006-03-30 | 2007-10-18 | Sumitomo Osaka Cement Co Ltd | Method for cleaning contaminated soil |
JP2009185159A (en) * | 2008-02-05 | 2009-08-20 | Yoshizawa Lime Industry | Soil-improving material and soil-improving method |
JP2010005488A (en) * | 2008-06-24 | 2010-01-14 | Taiheiyo Cement Corp | Method of evaluating heavy metal insolubilization performance of magnesium oxide |
JP2011131115A (en) * | 2009-12-22 | 2011-07-07 | Kagawa Univ | Sludge treating agent and sludge treatment method |
JP2012087017A (en) * | 2010-10-20 | 2012-05-10 | Atelier Tekuto:Kk | Method for constructing soil structure, and soil structure |
CN102923930A (en) * | 2012-11-09 | 2013-02-13 | 沈阳建筑大学 | Composite reagent in sludge chemical drying |
CN103817140A (en) * | 2014-02-28 | 2014-05-28 | 韩洪波 | Simple garbage water-separation method |
JP2015232224A (en) * | 2014-06-10 | 2015-12-24 | ジェコス株式会社 | Construction system of underground continuous wall |
JP2017048272A (en) * | 2015-08-31 | 2017-03-09 | 太平洋セメント株式会社 | Soil improvement stuff and soil improvement method |
JP2017221921A (en) * | 2016-06-17 | 2017-12-21 | 太平洋セメント株式会社 | Treatment method of mud generated in shield method |
JP2018105028A (en) * | 2016-12-27 | 2018-07-05 | 常郎 後藤 | Ground improvement method |
JP6363281B1 (en) * | 2017-08-31 | 2018-07-25 | テクニカ合同株式会社 | One-pack type neutral solidifying agent |
CN109796984A (en) * | 2017-11-16 | 2019-05-24 | 永清环保股份有限公司 | A kind of reduction stabilization agent for chromium-polluted soil |
CN111171822A (en) * | 2020-01-07 | 2020-05-19 | 扬州工业职业技术学院 | Preparation method of zeolite modified shell activated carbon and application of zeolite modified shell activated carbon in improvement of farmland soil and reduction of pollution and emission of non-point source |
CN113583682A (en) * | 2020-08-26 | 2021-11-02 | 中国科学院华南植物园 | Alkali-controlling conditioner for reducing alkalinity of coral sand and application thereof |
-
2001
- 2001-07-12 JP JP2001212678A patent/JP2002206090A/en active Pending
Cited By (33)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002167582A (en) * | 2000-11-29 | 2002-06-11 | Matsuda Giken Kogyo Kk | Soil stabilizer |
JP4564647B2 (en) * | 2000-11-29 | 2010-10-20 | 松田技研工業株式会社 | Soil solidifying agent |
JP2003117532A (en) * | 2001-10-09 | 2003-04-22 | Taiheiyo Cement Corp | Solidifying material and solidifying method for suppressing elution of heavy metal |
JP2003334526A (en) * | 2002-05-21 | 2003-11-25 | Konoike Constr Ltd | Method for solidifying and insolubilizing polluted soil, or the like |
JP2004131550A (en) * | 2002-10-09 | 2004-04-30 | Mitsubishi Materials Corp | Method for producing granulated soil |
JP2004203962A (en) * | 2002-12-24 | 2004-07-22 | Kurita Water Ind Ltd | Mud-solidifying agent and solidifying method |
JPWO2004078374A1 (en) * | 2003-03-03 | 2006-06-08 | 日本板硝子株式会社 | Soil conditioner |
JP2004292568A (en) * | 2003-03-26 | 2004-10-21 | Taiheiyo Cement Corp | Soil solidifying material |
JP2005002190A (en) * | 2003-06-11 | 2005-01-06 | Mirai Kensetsu Kogyo Kk | Soil improving material safe for marine organism and method for evaluating safety thereof |
JP2005007256A (en) * | 2003-06-18 | 2005-01-13 | Matsuda Giken Kogyo Kk | Contaminated soil insolubilization solidification agent |
JP2005028343A (en) * | 2003-07-11 | 2005-02-03 | Takenaka Komuten Co Ltd | Method for preventing elution of harmful metal from harmful metal contaminated waste product |
JP2005113065A (en) * | 2003-10-10 | 2005-04-28 | Kajima Corp | Consolidating agent for ground improvement and ground improvement method of construction |
JP2006000692A (en) * | 2004-06-15 | 2006-01-05 | Konoike Constr Ltd | Treatment method for dehydrating/hardening dredged soil or the like |
JP2006026472A (en) * | 2004-07-13 | 2006-02-02 | Asahi Kagaku Kogyo Co Ltd | Method for neutralizing alkali soil and leachate from the soil |
JP4590222B2 (en) * | 2004-07-13 | 2010-12-01 | 朝日化学工業株式会社 | Method for neutralizing alkaline soil and leachate from the soil |
JP2006219547A (en) * | 2005-02-09 | 2006-08-24 | Matsuda Giken Kogyo Kk | Soil-solidifying material |
JP2007268382A (en) * | 2006-03-30 | 2007-10-18 | Sumitomo Osaka Cement Co Ltd | Method for cleaning contaminated soil |
JP2009185159A (en) * | 2008-02-05 | 2009-08-20 | Yoshizawa Lime Industry | Soil-improving material and soil-improving method |
JP2010005488A (en) * | 2008-06-24 | 2010-01-14 | Taiheiyo Cement Corp | Method of evaluating heavy metal insolubilization performance of magnesium oxide |
JP2011131115A (en) * | 2009-12-22 | 2011-07-07 | Kagawa Univ | Sludge treating agent and sludge treatment method |
JP2012087017A (en) * | 2010-10-20 | 2012-05-10 | Atelier Tekuto:Kk | Method for constructing soil structure, and soil structure |
CN102923930A (en) * | 2012-11-09 | 2013-02-13 | 沈阳建筑大学 | Composite reagent in sludge chemical drying |
CN103817140A (en) * | 2014-02-28 | 2014-05-28 | 韩洪波 | Simple garbage water-separation method |
JP2015232224A (en) * | 2014-06-10 | 2015-12-24 | ジェコス株式会社 | Construction system of underground continuous wall |
JP2017048272A (en) * | 2015-08-31 | 2017-03-09 | 太平洋セメント株式会社 | Soil improvement stuff and soil improvement method |
JP2017221921A (en) * | 2016-06-17 | 2017-12-21 | 太平洋セメント株式会社 | Treatment method of mud generated in shield method |
JP2018105028A (en) * | 2016-12-27 | 2018-07-05 | 常郎 後藤 | Ground improvement method |
JP6363281B1 (en) * | 2017-08-31 | 2018-07-25 | テクニカ合同株式会社 | One-pack type neutral solidifying agent |
JP2019044054A (en) * | 2017-08-31 | 2019-03-22 | テクニカ合同株式会社 | One component type neutral solidification agent |
CN109796984A (en) * | 2017-11-16 | 2019-05-24 | 永清环保股份有限公司 | A kind of reduction stabilization agent for chromium-polluted soil |
CN109796984B (en) * | 2017-11-16 | 2020-12-04 | 永清环保股份有限公司 | Reduction stabilizing agent for chromium-contaminated soil |
CN111171822A (en) * | 2020-01-07 | 2020-05-19 | 扬州工业职业技术学院 | Preparation method of zeolite modified shell activated carbon and application of zeolite modified shell activated carbon in improvement of farmland soil and reduction of pollution and emission of non-point source |
CN113583682A (en) * | 2020-08-26 | 2021-11-02 | 中国科学院华南植物园 | Alkali-controlling conditioner for reducing alkalinity of coral sand and application thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP2002206090A (en) | Neutral soil-solidifying agent and method of improving ground and the like, and means for preventing elution of heavy metal | |
CN105107824A (en) | Harmless treatment method for drilling wastes of oil and gas fields | |
Pu et al. | An integrated method for the rapid dewatering and solidification/stabilization of dredged contaminated sediment with a high water content | |
KR100956593B1 (en) | Manufacturing method of artificial soil by solidifying organic or inorganic sludge | |
JP6357024B2 (en) | Sludge site stabilization method | |
CN103787475A (en) | Efficient wastewater treatment agent | |
KR100872058B1 (en) | Processing device of high-density slurry happening in construction working place | |
Al-Tabbaa et al. | Part I: Binders and Technologies—Basic Principles | |
JP3455952B2 (en) | How to fix harmful substances | |
JP2007014881A (en) | Recycling method of concrete mass | |
CN104086070A (en) | Sludge curing agent with high water content | |
SK278384B6 (en) | Manufacturing process of underground tightening wall | |
JPH0716599A (en) | Method for making waste containing harmful heavy metal harmless and stable | |
KR20070111065A (en) | Impermeable and semi-permeable reactive barrier and contaminant removal and cut-off by them | |
JP4084681B2 (en) | Sand-capping structure and sand-capping method | |
KR100590392B1 (en) | Preparing method of soil solidifier and solidifying soil thereof | |
JP2008155069A (en) | Method for manufacturing earth and sand alternative material using organic sludge as main raw material | |
JP3235019B2 (en) | Construction sludge regeneration treatment method | |
JP3220202B2 (en) | Wastewater treatment method for construction | |
JP2002029812A (en) | Method of reducing eluting quantity of heavy metal in cement-based solidified soil using artificial zeolite | |
JP2006055724A (en) | Method for soil restoration | |
JP3993776B2 (en) | Solidification method of contaminated soil | |
JP3897553B2 (en) | Construction method of underground purification wall | |
JP3156037B2 (en) | How to recycle construction sludge | |
JP3909479B2 (en) | Deodorizing and solidifying material construction method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 20031224 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20040122 |
|
A711 | Notification of change in applicant |
Free format text: JAPANESE INTERMEDIATE CODE: A711 Effective date: 20040122 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A821 Effective date: 20040122 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20040312 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20040402 |
|
A911 | Transfer to examiner for re-examination before appeal (zenchi) |
Free format text: JAPANESE INTERMEDIATE CODE: A911 Effective date: 20040511 |
|
A912 | Re-examination (zenchi) completed and case transferred to appeal board |
Free format text: JAPANESE INTERMEDIATE CODE: A912 Effective date: 20040611 |