JPH11278911A - Solidifying material - Google Patents
Solidifying materialInfo
- Publication number
- JPH11278911A JPH11278911A JP10083575A JP8357598A JPH11278911A JP H11278911 A JPH11278911 A JP H11278911A JP 10083575 A JP10083575 A JP 10083575A JP 8357598 A JP8357598 A JP 8357598A JP H11278911 A JPH11278911 A JP H11278911A
- Authority
- JP
- Japan
- Prior art keywords
- weight
- soil
- gypsum
- parts
- strength
- 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.)
- Granted
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B28/00—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
- C04B28/02—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing hydraulic cements other than calcium sulfates
- C04B28/021—Ash cements, e.g. fly ash cements ; Cements based on incineration residues, e.g. alkali-activated slags from waste incineration ; Kiln dust cements
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B7/00—Hydraulic cements
- C04B7/24—Cements from oil shales, residues or waste other than slag
- C04B7/243—Mixtures thereof with activators or composition-correcting additives, e.g. mixtures of fly ash and alkali activators
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2111/00—Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
- C04B2111/00474—Uses not provided for elsewhere in C04B2111/00
- C04B2111/00732—Uses not provided for elsewhere in C04B2111/00 for soil stabilisation
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/10—Production of cement, e.g. improving or optimising the production methods; Cement grinding
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Combustion & Propulsion (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
- Curing Cements, Concrete, And Artificial Stone (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、都市ゴミ焼却灰や
下水汚泥焼却灰等の廃棄物を原料として製造してなる焼
成物(以下、エコセメントクリンカーという)と石膏及
び石灰を使用した固化材に係わり、特に、残土改良及び
火山灰質粘性土の固化に適した固化材に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a fired material (hereinafter referred to as "eco-cement clinker") produced from waste such as incinerated ash of municipal waste and incinerated ash of sewage sludge, and a solidified material using gypsum and lime. In particular, the present invention relates to a solidified material suitable for improvement of residual soil and solidification of volcanic ash clayey soil.
【0002】[0002]
【従来の技術】地下道、地下鉄、共同溝などの大型土
工、建築物の地下開削工事、電気、電話、ガス、上下水
道等の敷設工事に際しては、大量の残土が発生する。こ
の内、粘性土は、その性状からハンドリングが悪く、固
化材等で処理している。また、粘性土も含め他の砂質系
の土質も、建設発生土の有効利用の観点から、残土を固
化材等で改良して様々な用途に有効利用するケースが増
大している。2. Description of the Related Art A large amount of residual soil is generated in large-scale earthworks such as underpasses, subways, and common ditches, underground excavation work for buildings, and laying work for electricity, telephone, gas, water and sewage. Of these, the cohesive soil is poorly handled due to its properties and is treated with a solidifying material or the like. Also, from the viewpoint of effective use of construction-generated soil, the cases of improving the remaining soil with a solidifying material or the like and effectively utilizing it for various applications are increasing for other sandy soils including cohesive soil.
【0003】また、日本では、火山が多く、各地に火山
灰起源の土が分布している。国土の狭い日本では、地盤
の性状に関わらず道路、工場、宅地等の開発が行われて
いる。火山灰質粘性土は、自然状態では、しっかりした
土層を形成しているが、土工機械等により一旦乱される
と軟弱化し、施工が困難となるばかりでなく、地盤とし
ての支持力も大幅に低下するため、固化材等による改良
が一般に行われている。[0003] In Japan, there are many volcanoes, and soils of volcanic ash origin are distributed in various places. In Japan, where the land is narrow, roads, factories, residential lands and the like are being developed regardless of the nature of the ground. Volcanic ashy clay soil forms a solid soil layer in its natural state, but once it is disturbed by earth-moving machinery etc., it becomes soft and not only difficult to construct, but also greatly reduces the bearing capacity of the ground Therefore, improvement with a solidifying material or the like is generally performed.
【0004】これらの固化材として、一般のセメントあ
るいはセメント系固化材も用いられるが、残土処理及び
火山灰質粘土の改良に関しては生石灰や消石灰が効果的
であると言われている。As these solidifying materials, general cement or cement-based solidifying materials are also used, but quick lime and slaked lime are said to be effective for the treatment of residual soil and improvement of volcanic ash clay.
【0005】しかし、生石灰は、土中の水分と反応して
激しい発熱とこれに伴う水蒸気を発生すること、また、
生石灰の微粉、乾いた土の飛散により、市街地での使用
には制約がある。更に、生石灰は通常、塊状で使用され
るため、対象土と混合して消化が終了した後、再度混合
する必要があり、施工手間がかかる。一方、消石灰は、
土と石灰のポゾラン反応により強度が増加するが、この
反応は、長期に起こるものであり、短期間で所定の強度
を発現させるためには不都合である。更に、高い強度が
要求される場合には、生石灰に比較して多量の消石灰が
必要となり、不経済である。これらの問題を解決するた
めに、粉末の生石灰を用い、石灰含有率を低下させ、か
つポルトランドセメントと石膏を配合した固化材が開示
されている(例えば特許第8−2503771号)。ま
た、セメント、石灰、石膏を主成分とした他の固化材も
提案されている(例えば、特公昭63−45276号、
特公昭58−57379号等)。しかし、これらに用い
られるセメントの原料である石灰石や粘土は、限りある
資源である。[0005] However, quicklime reacts with water in the soil to generate violent heat and accompanying water vapor.
The use in urban areas is limited by the fine powder of quicklime and the scattering of dry soil. Furthermore, since quick lime is usually used in a lump, it needs to be mixed with the target soil and digested again, and then mixed again, which takes a lot of work. On the other hand, slaked lime is
Although the strength increases due to the pozzolanic reaction between soil and lime, this reaction occurs over a long period of time, which is inconvenient for achieving a predetermined strength in a short period of time. Further, when high strength is required, a large amount of slaked lime is required as compared with quick lime, which is uneconomical. In order to solve these problems, there has been disclosed a solidified material that uses powdered lime, reduces the lime content, and mixes Portland cement and gypsum (for example, Japanese Patent No. 8-2503771). Further, other solidifying materials mainly containing cement, lime, and gypsum have been proposed (for example, Japanese Patent Publication No. 63-45276,
JP-B-58-57379, etc.). However, limestone and clay, which are the raw materials of cement used for these, are limited resources.
【0006】一方、近年、都市ゴミや下水汚泥等の一般
廃棄物及び産業廃棄物は著しく増加し、廃棄物の有効利
用、再資源化が各方面で試みられているが、廃棄物処理
に関する決定的な方法はなく、現状は、埋め立てに頼っ
ている。しかし、最近、セメントの製造分野では、廃棄
物の有効利用及び再資源化を目的として、都市ゴミ焼却
灰や下水汚泥焼却灰等の廃棄物を原料とした焼成物(以
下「エコセメントクリンカー」という)が製造されてい
る。On the other hand, in recent years, general waste and industrial waste such as municipal waste and sewage sludge have increased remarkably, and effective use and recycling of waste have been attempted in various fields. There is no traditional method, and at present, it depends on landfill. However, recently, in the field of cement production, in order to effectively use and recycle waste, fired products made from waste such as incinerated ash from municipal waste and incinerated ash from sewage sludge (hereinafter referred to as “Eco-cement clinker”) ) Is manufactured.
【0007】[0007]
【発明が解決しようとする課題】従って、本発明の目的
は、固化材として満足できる性能を具備しかつ、限りあ
る資源を大切にするため、廃棄物の有効利用及び再資源
化が図れるエコセメントクリンカーを利用し得る固化材
を提供することにある。SUMMARY OF THE INVENTION Accordingly, an object of the present invention is to provide an eco-cement which has satisfactory performance as a solidifying material, and in which a limited amount of resources is cherished so that waste can be effectively used and recycled. An object of the present invention is to provide a solidifying material that can utilize clinker.
【0008】[0008]
【課題を解決するための手段】斯かる実情に鑑み本発明
者は鋭意研究を行った結果、上記エコセメントクリンカ
ーに、一定量の石膏及び石灰を混合した固化材が、含水
比の低減効果が高く、また火山灰質粘性土等の有機土壌
に対しても有効であり、早期に高い強度を発現すること
を見出し、本発明を完成した。Means for Solving the Problems In view of such circumstances, the inventors of the present invention have conducted intensive studies, and as a result, a solidified material obtained by mixing a certain amount of gypsum and lime with the above-mentioned eco-cement clinker has an effect of reducing the water content. The present invention was found to be high and effective for organic soils such as volcanic ash clayey soil, and to exhibit high strength at an early stage, and completed the present invention.
【0009】すなわち本発明は、都市ゴミ焼却灰及び下
水汚泥焼却灰から選ばれる1種又は2種以上を原料と
し、C11A7CaCl2、C11A7CaF2及びC3Aの1
種又は2種以上を10〜40重量%含有し、かつC2S
及び/又はC3Sを含有する焼成物100重量部に対
し、石膏5〜50重量部と生石灰及び/又は消石灰10
〜60重量部とを混合したことを特徴とする固化材を提
供するものである。That is, the present invention uses one or more of municipal waste incineration ash and sewage sludge incineration ash as raw materials, and comprises one of C 11 A 7 CaCl 2 , C 11 A 7 CaF 2 and C 3 A.
10 to 40% by weight of at least one species or two or more species, and C 2 S
And / or 100 parts by weight of the calcined material containing C 3 S, 5 to 50 parts by weight of gypsum, and quicklime and / or slaked lime 10
And to 60 parts by weight.
【0010】[0010]
【発明の実施の形態】本発明で用いられるエコセメント
クリンカーは、都市ゴミ焼却灰及び下水汚泥焼却灰から
選ばれる1種又は2種以上を原料とし、11CaO・7
Al2O3・CaCl2(C11A7CaCl2)、11Ca
O・7Al2O3・CaF2(C11A7CaF2)、及び3
CaO・Al2O3(C3A)の1種又は2種以上を10
〜40重量%含有し、かつ2CaO・SiO2(C2S)
及び/又は3CaO・SiO2(C3S)を含有する焼成
物である。なお、これに石膏を加えたものはエコセメン
トと称する。BEST MODE FOR CARRYING OUT THE INVENTION The eco-cement clinker used in the present invention is composed of at least one material selected from municipal garbage incineration ash and sewage sludge incineration ash.
Al 2 O 3 .CaCl 2 (C 11 A 7 CaCl 2 ), 11Ca
O · 7Al 2 O 3 · CaF 2 (C 11 A 7 CaF 2), and 3
One or more of CaO.Al 2 O 3 (C 3 A)
Containing 40 wt%, and 2CaO · SiO 2 (C 2 S )
And / or 3CaO.SiO 2 (C 3 S). In addition, what added gypsum to this is called ecocement.
【0011】このエコセメントクリンカーの原料は貝殻
や下水汚泥に生石灰を混合した下水汚泥乾粉、その他の
一般廃棄物や産業廃棄物、更には普通のセメント原料で
ある石灰石、粘土、珪石、アルミ灰、ボーキサイト、鉄
等と混合して成分調整した原料であってもよい。The raw material of this eco-cement clinker is sewage sludge dry powder obtained by mixing quicklime with shells and sewage sludge, other general wastes and industrial wastes, and limestone, clay, silica stone, aluminum ash, and other ordinary cement raw materials. It may be a raw material whose components are adjusted by mixing with bauxite, iron or the like.
【0012】本発明の固化材は、上記の原料を1200
〜1500℃で焼成したクリンカー(エコセメントクリ
ンカー)を粉砕後、石膏及び石灰を混合し製造される。[0012] The solidified material of the present invention is obtained by mixing the above raw materials with 1200
It is manufactured by pulverizing clinker (eco-cement clinker) fired at 11500 ° C. and then mixing gypsum and lime.
【0013】上記焼成物のC11A7CaCl2、C11A7
CaF2及びC3Aのアルミニウム源は、主に焼却灰に由
来するものであるが、これらの焼成物中の含有量が10
重量%未満の場合は、焼却灰の使用量が少ないこととな
り、これらの有効利用及び再資源化の観点から好ましく
ない。一方、これが40重量%を超えると、水和の進行
により、過大な膨張を起こすことがあり、好ましくな
い。C 11 A 7 CaCl 2 , C 11 A 7
The aluminum sources of CaF 2 and C 3 A are mainly derived from incinerated ash, but their content in the fired product is 10%.
When the amount is less than% by weight, the amount of incinerated ash used is small, which is not preferable from the viewpoint of effective utilization and recycling. On the other hand, if it exceeds 40% by weight, excessive swelling may occur due to the progress of hydration, which is not preferable.
【0014】焼成物中には、C2S及び/又はC3Sを含
有することが必要である。これは、C2S及び/又はC3
Sが水和によりカルシウムシリケート水和物を生じ、長
期的に安定な強度をもたらすからである。It is necessary that the calcined product contains C 2 S and / or C 3 S. This is because C 2 S and / or C 3
This is because S forms calcium silicate hydrate by hydration and provides stable strength in the long term.
【0015】本発明に用いる石膏は、無水石膏、二水石
膏、半水石膏のいずれも使用できるが、強度の発現性及
び改良体の安定性の面から、溶解速度の遅い無水石膏が
好ましい。石膏は、エコセメントクリンカー100重量
部に対して5〜50重量部添加するのが好ましい。5重
量部未満では、強度発現性が乏しく、また、50重量部
を超えると強度発現も低くなるばかりでなく、改良体の
膨張による安定性の低下が生じることがある。特に好ま
しい範囲は、エコセメントクリンカー100重量部に対
して、10〜40重量部である。As the gypsum used in the present invention, any of anhydrous gypsum, gypsum dihydrate and hemihydrate gypsum can be used, but anhydrous gypsum having a low dissolution rate is preferred from the viewpoint of the development of strength and the stability of the improved body. Gypsum is preferably added in an amount of 5 to 50 parts by weight based on 100 parts by weight of Ecocement Clinker. If the amount is less than 5 parts by weight, the strength expression is poor. If the amount exceeds 50 parts by weight, not only the strength expression is reduced, but also the stability of the improved product may be reduced due to expansion. A particularly preferred range is 10 to 40 parts by weight based on 100 parts by weight of Ecocement Clinker.
【0016】本発明に用いる生石灰及び/又は消石灰
は、エコセメントクリンカー100重量部に対して10
〜60重量部添加するのが好ましい。10重量部未満で
は、含水比の低減効果が少ないことに加え、強度発現性
も低下する。また、60重量部を超えると石灰を単独で
用いた場合のような問題点が発生するばかりでなく、残
土改良に用いた場合には粘性土以外の土質の強度発現性
が低下する。特に好ましい範囲は、エコセメントクリン
カー100重量部に対して、20〜50重量部である。The quick lime and / or slaked lime used in the present invention is 10 parts by weight per 100 parts by weight of Ecocement Clinker.
It is preferable to add 〜60 parts by weight. If the amount is less than 10 parts by weight, the effect of reducing the water content is small and the strength developability is also reduced. On the other hand, if the amount exceeds 60 parts by weight, not only problems such as the case where lime is used alone occur, but also if it is used for improving the remaining soil, the strength development of soil other than the clayey soil is reduced. A particularly preferred range is 20 to 50 parts by weight based on 100 parts by weight of Ecocement Clinker.
【0017】生石灰は、土中の水分と反応し、消石灰と
なって水を吸収するとともに、消化反応による発熱で水
分を蒸発させ、含水量の低下をもたらせる。また、消化
による体積膨張により周囲の土への圧密効果を及ぼす。
更に、生石灰、消石灰は、水への溶解により生じるカル
シウムイオンが土粒子表面に吸着し、凝集を促すととも
に、長期的には、土粒子と石灰とのポゾラン反応によっ
て強度増加に寄与する。従って、生石灰の方が消石灰よ
りも効果が高いが、固化材に水を加えてスラリーとして
使用する場合には消石灰が適する。Quick lime reacts with water in the soil to become slaked lime and absorbs water, and at the same time, evaporates the water due to heat generated by the digestion reaction, thereby reducing the water content. In addition, the volume expansion due to digestion exerts a consolidation effect on the surrounding soil.
Further, in quicklime and slaked lime, calcium ions generated by dissolution in water are adsorbed on the surface of soil particles to promote aggregation, and in the long term, contribute to increase in strength by a pozzolan reaction between the soil particles and lime. Therefore, although quick lime is more effective than slaked lime, slaked lime is suitable when slurry is used by adding water to the solidified material.
【0018】[0018]
【発明の効果】エコセメントクリンカー中のC11A7C
aCl2、C11A7CaF2、C3Aは添加する石膏とで水
和物としてエトリンガイトを生成する。更に、C2S、
C3Sの水和及び生石灰の消化によって生じるCa(O
H)2を消費するかたちでもエトリンガイトを生成す
る。このエトリンガイトは、自重の約45%が結晶水で
あることから、見掛けの含水量の低下と高い強度発現性
を示す効果がある。また、エトリンガイトの生成反応
は、有機物の存在下でも順調に進行するため、有機土壌
に対しても非常に有効である。更に、エコセメントクリ
ンカー中のC11A7CaCl2、C11A7CaF2、C3A
がエトリンガイトを生成する反応は、他のセメント鉱物
よりも極めて早く、早期の強度発現に有効である。な
お、C2S、C3Sの水和によるカルシウムシリケート水
和物の生成により、長期的な強度も安定して確保でき
る。また石灰は、長期的に強度増加に寄与する。従っ
て、本発明の固化材は、資源の有効利用が図れるのみな
らず、固化材としての性能にも優れる。EFFECT OF THE INVENTION C 11 A 7 C in Ecocement Clinker
aCl 2 , C 11 A 7 CaF 2 and C 3 A form ettringite as a hydrate with the added gypsum. Further, C 2 S,
Ca (O) produced by hydration of C 3 S and digestion of quicklime
H) also produces ettringite in the form of consuming 2 ; Since ettringite has about 45% of its own weight as water of crystallization, it has an effect of reducing the apparent water content and exhibiting high strength. In addition, since the ettringite formation reaction proceeds smoothly even in the presence of organic matter, it is very effective for organic soil. Further, C 11 A 7 CaCl 2 , C 11 A 7 CaF 2 , C 3 A in ecocement clinker
The reaction that produces ettringite is much faster than other cement minerals, and is effective for early strength development. In addition, long-term strength can be stably secured by the generation of calcium silicate hydrate by hydration of C 2 S and C 3 S. Lime also contributes to an increase in strength in the long term. Therefore, the solidified material of the present invention not only can effectively utilize resources but also has excellent performance as a solidified material.
【0019】[0019]
【実施例】以下、実施例を挙げて本発明を更に詳細に説
明するが、本発明は、これらに限定されるものではな
い。EXAMPLES Hereinafter, the present invention will be described in more detail by way of examples, but the present invention is not limited thereto.
【0020】実施例1 表1に示す乾燥した都市ゴミ焼却灰29.7重量%、石
灰石粉68.6重量%、アルミ灰1.5重量%、粘土
0.2重量%を原料として、ロータリーキルンを用いて
1300〜1450℃でエコセメントクリンカーを焼成
した。得られたクリンカーは、縦型ミルでブレーン比表
面積が4000cm2/gとなるよう粉砕した。この鉱物
組成を表2に示す。EXAMPLE 1 A rotary kiln was prepared using 29.7% by weight of dried municipal incineration ash, 68.6% by weight of limestone powder, 1.5% by weight of aluminum ash and 0.2% by weight of clay shown in Table 1. Was used to fire Ecocement Clinker at 1300-1450 ° C. The obtained clinker was pulverized by a vertical mill so that the Blaine specific surface area became 4000 cm 2 / g. Table 2 shows the mineral composition.
【0021】[0021]
【表1】 [Table 1]
【0022】[0022]
【表2】 [Table 2]
【0023】このエコセメントクリンカーの粉砕物(エ
コ粉砕物)と粒径3mm以下の生石灰及び比表面積4,0
00cm2/gの無水石膏を用いて表3に示す配合の固化
材を試製した。The pulverized product of the eco-cement clinker (eco-pulverized product), quicklime having a particle size of 3 mm or less, and a specific surface area of 4.00
A solidified material having the composition shown in Table 3 was trial-produced using anhydrous gypsum of 00 cm 2 / g.
【0024】表4に示す性状の砂質土及び関東ロームを
用い、表3のそれぞれの固化材を砂質土で4%、関東ロ
ームで12%(いずれも湿潤試料に対する外割重量百分
率)添加混合した。混練物は、5φ×10cm及びCBR
モールドに成型後、20℃にて所定材齢まで養生し、一
軸圧縮強さ及び水浸膨張量を求めた。混練は、ホバート
ミキサーにて5分間行った。また、一軸圧縮強さは地盤
工学会基準(JGST 511)、水浸膨張量は地盤工
学会基準(JGS T 721)により求めた。結果を
表3に示す。Using the sandy soil and the Kanto loam having the properties shown in Table 4, the respective solidifying materials shown in Table 3 were added to the sandy soil by 4% and the Kanto loam by 12% (all in terms of percentage by weight based on the wet sample). Mixed. The kneaded material is 5φ × 10cm and CBR
After being molded into a mold, it was cured at 20 ° C. to a predetermined material age, and the uniaxial compressive strength and the amount of water immersion expansion were determined. The kneading was performed with a Hobart mixer for 5 minutes. The uniaxial compressive strength was determined according to the Japan Geotechnical Society standard (JGST 511), and the amount of water immersion and expansion was determined according to the Japanese Geotechnical Society standard (JGS T 721). Table 3 shows the results.
【0025】[0025]
【表3】 [Table 3]
【0026】[0026]
【表4】 [Table 4]
【0027】以上の結果から石膏配合量が少ないと膨張
量は少ないものの、強度発現性が乏しく、また、砂質土
の場合、配合量に伴う強度の変動幅がロームよりも大き
いことが判る。これに対し、石膏配合量が多い場合にも
強度が低下し、これに加えて膨張量が多くなる。なお、
含水比の低い砂質土の方が大きな膨張を示す。一方、生
石灰の配合量が少ないと、強度発現性が低く、特にロー
ムの方がその影響を大きく受ける。生石灰の配合量が多
い場合には、ロームでは強度が高くなる傾向にあるもの
の、砂質土では大きく低下する。また、膨張量も生石灰
量を多くすることで大きくなるが、石膏を増量した場合
と比較するとその程度は小さいことが判る。From the above results, it can be seen that if the amount of gypsum is small, the expansion amount is small, but the strength development is poor, and in the case of sandy soil, the fluctuation width of the strength according to the amount is larger than that of loam. On the other hand, when the amount of the gypsum is large, the strength is reduced, and in addition, the expansion amount is increased. In addition,
Sandy soils with a low water content show greater expansion. On the other hand, if the amount of quick lime is small, the strength development is low, and particularly, the loam is more affected by the effect. When the amount of quick lime is large, the strength tends to be high in the loam, but greatly decreases in the sandy soil. In addition, the amount of swelling is increased by increasing the amount of quicklime, but it can be seen that the degree is smaller than when gypsum is increased.
フロントページの続き (51)Int.Cl.6 識別記号 FI //(C04B 28/14 B09B 3/00 304G 7:28 22:06) (C04B 28/02 7:28 22:14 22:06) C09K 103:00 Continued on the front page (51) Int.Cl. 6 Identification symbol FI // (C04B 28/14 B09B 3/00 304G 7:28 22:06) (C04B 28/02 7:28 22:14 22:06) C09K 103: 00
Claims (1)
選ばれる1種又は2種以上を原料とし、C11A7CaC
l2、C11A7CaF2及びC3Aの1種又は2種以上を1
0〜40重量%含有し、かつC2S及び/又はC3Sを含
有する焼成物100重量部に対し、石膏5〜50重量部
と生石灰及び/又は消石灰10〜60重量部とを混合し
たことを特徴とする固化材。1. A method comprising using one or more selected from municipal refuse incineration ash and sewage sludge incineration ash as a raw material, and comprising C 11 A 7 CaC
one or more of l 2 , C 11 A 7 CaF 2 and C 3 A
Contains 0 to 40 wt%, and with respect to the calcined product 100 parts by weight containing C 2 S and / or C 3 S, was mixed with the gypsum 5-50 parts by weight quicklime and / or slaked lime 10 to 60 parts by weight A solidified material characterized by the following.
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JP08357598A JP4112666B2 (en) | 1998-03-30 | 1998-03-30 | Solidified material |
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JP08357598A JP4112666B2 (en) | 1998-03-30 | 1998-03-30 | Solidified material |
Publications (2)
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JPH11278911A true JPH11278911A (en) | 1999-10-12 |
JP4112666B2 JP4112666B2 (en) | 2008-07-02 |
Family
ID=13806314
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Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2003071425A (en) * | 2001-09-05 | 2003-03-11 | Japan Organo Co Ltd | Treating method for chemical contaminant |
JP2009285590A (en) * | 2008-05-30 | 2009-12-10 | Toa Grout Kogyo Co Ltd | Engineering method of neutral solidification of mud and novel gypsum-based solidification improving material |
JP2016169262A (en) * | 2015-03-11 | 2016-09-23 | 太平洋セメント株式会社 | Solidifying material and production method therefor |
JP2016169260A (en) * | 2015-03-11 | 2016-09-23 | 太平洋セメント株式会社 | Solidifying material and production method therefor |
JP2018104213A (en) * | 2016-12-22 | 2018-07-05 | 宇部興産株式会社 | Cement composition and manufacturing method therefor and soil improvement method |
KR20210124802A (en) * | 2020-04-07 | 2021-10-15 | 김동경 | Recycling aggregate and Solidification agent manufacturing method utilizing incineration agent |
-
1998
- 1998-03-30 JP JP08357598A patent/JP4112666B2/en not_active Expired - Fee Related
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2003071425A (en) * | 2001-09-05 | 2003-03-11 | Japan Organo Co Ltd | Treating method for chemical contaminant |
JP2009285590A (en) * | 2008-05-30 | 2009-12-10 | Toa Grout Kogyo Co Ltd | Engineering method of neutral solidification of mud and novel gypsum-based solidification improving material |
JP2016169262A (en) * | 2015-03-11 | 2016-09-23 | 太平洋セメント株式会社 | Solidifying material and production method therefor |
JP2016169260A (en) * | 2015-03-11 | 2016-09-23 | 太平洋セメント株式会社 | Solidifying material and production method therefor |
JP2018104213A (en) * | 2016-12-22 | 2018-07-05 | 宇部興産株式会社 | Cement composition and manufacturing method therefor and soil improvement method |
KR20210124802A (en) * | 2020-04-07 | 2021-10-15 | 김동경 | Recycling aggregate and Solidification agent manufacturing method utilizing incineration agent |
Also Published As
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JP4112666B2 (en) | 2008-07-02 |
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