JP2001199750A - Hydraulic calcium silicate-based raw material using ALC building waste and method for producing the same - Google Patents
Hydraulic calcium silicate-based raw material using ALC building waste and method for producing the sameInfo
- Publication number
- JP2001199750A JP2001199750A JP2000006027A JP2000006027A JP2001199750A JP 2001199750 A JP2001199750 A JP 2001199750A JP 2000006027 A JP2000006027 A JP 2000006027A JP 2000006027 A JP2000006027 A JP 2000006027A JP 2001199750 A JP2001199750 A JP 2001199750A
- Authority
- JP
- Japan
- Prior art keywords
- alc
- raw material
- calcium silicate
- waste
- based raw
- 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
- 239000002699 waste material Substances 0.000 title claims abstract description 38
- 239000002994 raw material Substances 0.000 title claims abstract description 30
- 239000000378 calcium silicate Substances 0.000 title claims abstract description 29
- 229910052918 calcium silicate Inorganic materials 0.000 title claims abstract description 29
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical compound [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 title claims abstract description 29
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 11
- MKTRXTLKNXLULX-UHFFFAOYSA-P pentacalcium;dioxido(oxo)silane;hydron;tetrahydrate Chemical compound [H+].[H+].O.O.O.O.[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-][Si]([O-])=O.[O-][Si]([O-])=O.[O-][Si]([O-])=O.[O-][Si]([O-])=O.[O-][Si]([O-])=O.[O-][Si]([O-])=O MKTRXTLKNXLULX-UHFFFAOYSA-P 0.000 claims abstract description 18
- 229910052500 inorganic mineral Inorganic materials 0.000 claims abstract description 9
- 239000011707 mineral Substances 0.000 claims abstract description 9
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims abstract description 6
- 239000000292 calcium oxide Substances 0.000 claims abstract description 5
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims abstract description 4
- 238000010438 heat treatment Methods 0.000 claims description 8
- 239000004035 construction material Substances 0.000 claims 1
- 239000000463 material Substances 0.000 abstract description 7
- 239000004568 cement Substances 0.000 abstract description 6
- 239000002440 industrial waste Substances 0.000 abstract description 4
- 239000004566 building material Substances 0.000 abstract description 3
- 230000009467 reduction Effects 0.000 abstract description 3
- 238000006467 substitution reaction Methods 0.000 abstract 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 12
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 8
- 235000010755 mineral Nutrition 0.000 description 7
- 239000004570 mortar (masonry) Substances 0.000 description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 6
- 239000011398 Portland cement Substances 0.000 description 6
- 239000010456 wollastonite Substances 0.000 description 5
- 229910052882 wollastonite Inorganic materials 0.000 description 5
- 229910000019 calcium carbonate Inorganic materials 0.000 description 4
- 239000000377 silicon dioxide Substances 0.000 description 4
- 235000012255 calcium oxide Nutrition 0.000 description 3
- 239000001569 carbon dioxide Substances 0.000 description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 description 3
- 239000011248 coating agent Substances 0.000 description 3
- 238000000576 coating method Methods 0.000 description 3
- 239000006260 foam Substances 0.000 description 3
- 229910021532 Calcite Inorganic materials 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 235000011116 calcium hydroxide Nutrition 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 230000036571 hydration Effects 0.000 description 2
- 238000006703 hydration reaction Methods 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000010908 plant waste Substances 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 239000004576 sand Substances 0.000 description 2
- 239000000741 silica gel Substances 0.000 description 2
- 229910002027 silica gel Inorganic materials 0.000 description 2
- -1 silicate ions Chemical class 0.000 description 2
- 239000004575 stone Substances 0.000 description 2
- 235000019738 Limestone Nutrition 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 238000002441 X-ray diffraction Methods 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000002950 deficient Effects 0.000 description 1
- 230000000779 depleting effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000011381 foam concrete Substances 0.000 description 1
- 239000004088 foaming agent Substances 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 150000004677 hydrates Chemical class 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 239000011268 mixed slurry Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000005192 partition Methods 0.000 description 1
- 230000009257 reactivity Effects 0.000 description 1
- 230000008439 repair process Effects 0.000 description 1
- 230000003252 repetitive effect Effects 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- 238000003746 solid phase reaction Methods 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
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
- C04B18/00—Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
- C04B18/04—Waste materials; Refuse
- C04B18/16—Waste materials; Refuse from building or ceramic industry
-
- 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
-
- 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
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Ceramic Engineering (AREA)
- Civil Engineering (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明が属する技術分野】本発明は、建築物の解体現場
などから発生するALC建築廃材の有効利用し、セメン
トなどの原料の一部となる水硬性の珪酸カルシウム系原
料とする技術に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a technology for effectively utilizing ALC building waste generated from a demolition site of a building, etc., and forming a hydraulic calcium silicate-based raw material which becomes a part of a raw material such as cement. is there.
【0002】[0002]
【従来の技術】一般に、ALC(軽量気泡コンクリー
ト)は、珪酸質原料としての天然の珪石や珪砂と、石灰
質原料としての天然原料から直接製造される石灰石やセ
メントを主原料とし、これらのスラリーを発泡硬化させ
た後、水蒸気養生することによって得られる。2. Description of the Related Art Generally, ALC (Lightweight Cellular Concrete) is mainly made of natural silica stone or silica sand as a siliceous raw material, and limestone or cement directly produced from a natural raw material as a calcareous raw material. It is obtained by foam curing and then steam curing.
【0003】即ち、上記の主原料に、副原料として石膏
の他、オートクレーブ前のALC切断屑などの繰り返し
原料を添加し、その配合物に水に加えて混合スラリーと
し、これにアルミニウム粉末のような発泡剤を添加し、
型枠に注入して発泡させる。更に所定時間経過して可塑
性状態となったときにピアノ線で所望寸法に切断し、そ
の後これをオートクレーブに入れて高温高圧で水蒸気養
成する。[0003] In other words, in addition to gypsum as a secondary raw material, a repetitive raw material such as ALC cutting waste before autoclave is added to the above main raw material, and the resulting mixture is added to water to form a mixed slurry. Add a foaming agent
Inject into foam and foam. Further, when the plastic state is reached after a predetermined time, the piece is cut into a desired size with a piano wire, and then put into an autoclave and steam-cured at high temperature and high pressure.
【0004】得られたALCは、所定寸法に切削加工す
ることによって、パネルなどの建築材料などとなる。建
築材料としてのALCパネルは、鉄骨造やRC造などの
外壁、間仕切り、屋根、床などの材料として広く使用さ
れている。[0004] The obtained ALC is cut into a predetermined size to be a building material such as a panel. ALC panels as building materials are widely used as materials for outer walls, partitions, roofs, floors and the like of steel structures and RC structures.
【0005】このALCの製造工場からは、寸法調整に
伴い発生する切削屑や切断屑、あるいは破損などによる
不良品のようなALC廃材が発生する。このALC製造
工場内で発生した廃材(以下、工場内廃材という)につ
いては、そのほとんど全量がALC製造工程内にて再利
用されている。[0005] From the ALC manufacturing factory, ALC waste such as cutting chips and cutting chips generated due to dimensional adjustment or defective products due to breakage is generated. Almost all of the waste material generated in the ALC manufacturing factory (hereinafter referred to as factory waste material) is reused in the ALC manufacturing process.
【0006】その方法としては、特に加熱処理などを行
わず、粉砕した工場内廃材をそのまま繰り返し原料とし
て用いることが通常行われている。そのほか、特開平5
−319876号公報には、工場内廃材を800〜15
00℃で焼成してゾノライト及びワラストナイトを主成
分とする粉粒体に変化させたものを、ALC製造工程内
で再利用することが提案されている。[0006] As the method, it is common practice to repeatedly use the pulverized waste material in the factory as it is without particularly performing heat treatment or the like. In addition, JP-A-5
No. 319876 discloses that waste materials in a factory are 800 to 15 times.
It has been proposed to recycle the powder which has been baked at 00 ° C. and converted into a powder mainly composed of zonolite and wollastonite in an ALC production process.
【0007】[0007]
【発明が解決しようとする課題】一方、建築物の建替え
や取り壊しに伴って発生するALC建築廃材は、ALC
が日本国内で製造が開始されてから30年以上が経過す
るため特に増加しつつあり、上記の工場内廃材に比べて
遥かに大量である。しかしながら、ALC建築廃材は、
その一部が破砕もしくは粉砕されて、路盤材や埋め立て
工事用として利用されているが、大部分のALC廃材は
再利用されることなく、産業廃棄物として処理されてい
た。On the other hand, ALC building waste generated with the rebuilding and demolition of buildings is ALC.
Since the production has been started in Japan, more than 30 years have passed, and the number of such wastes has been particularly increasing. However, ALC building waste is
Some of them are crushed or crushed and used for roadbed materials and landfill works. However, most of ALC waste materials were treated as industrial waste without being reused.
【0008】本発明は、このような従来の事情に鑑み、
建築物の解体現場から発生するALC建築廃材を再利用
して、産業廃棄物の削減に寄与するのみならず、新たな
珪酸カルシウム系原料及びその製造方法を提供すること
を目的とする。The present invention has been made in view of such a conventional situation,
It is an object of the present invention to provide a new calcium silicate-based raw material and a method for producing the same, not only contributing to the reduction of industrial waste by recycling ALC building waste generated from the demolition site of a building.
【0009】[0009]
【課題を解決するための手段】上記目的を達成するた
め、本発明は、ALC建築廃材を利用して、水硬性珪酸
カルシウム系原料を提供するものである。即ち、本発明
が提供する水硬性珪酸カルシウム系原料の製造方法は、
トバモライトの一部が炭酸化されたALC廃材を、60
0〜1500℃で加熱処理することを特徴とする。In order to achieve the above object, the present invention provides a hydraulic calcium silicate-based raw material using ALC building waste. That is, the method for producing a hydraulic calcium silicate-based raw material provided by the present invention comprises:
60 parts of ALC waste, which is partly carbonated with tobermorite,
The heat treatment is performed at 0 to 1500 ° C.
【0010】また、本発明が提供する水硬性珪酸カルシ
ウム系原料は、ALC建築廃材を600〜1500℃で
加熱処理して得られたものであり、酸化カルシウムと、
トバモライトの一部が分解した珪酸カルシウム系鉱物と
を含むことを特徴とする。[0010] The hydraulic calcium silicate-based raw material provided by the present invention is obtained by heat-treating ALC building waste at 600 to 1500 ° C.
It is characterized in that a part of tobermorite contains a decomposed calcium silicate mineral.
【0011】[0011]
【発明の実施の形態】ALCの主な硬性成分は、オート
クレーブ中で高温高圧の水蒸気養生を行うことにより生
成されるトバモライト(5CaO・6SiO2・5H
2O)と呼ばれる結晶性の珪酸カルシウム系水和物と、
未反応の珪石とからなる。このトラボライトは、水分の
存在下に空気中の炭酸ガスと反応して炭酸化されて、炭
酸カルシウム(CaCO3)とシリカゲルに分解する。The main hydraulic components of the embodiment of the invention] ALC is tobermorite produced by performing the high-temperature high-pressure steam curing in an autoclave (5CaO · 6SiO 2 · 5H
And crystalline calcium silicate hydrate called 2 O),
It consists of unreacted silica. This travolite reacts with carbon dioxide in the air in the presence of moisture to be carbonated, and is decomposed into calcium carbonate (CaCO 3 ) and silica gel.
【0012】ALC建築廃材中のトバモライトの炭酸化
の速度は、炭酸ガスの濃度のみならず、相対湿度、温
度、ALC含水量、ALC表面の処理状態(塗装の種
類、厚さ、補修)などにより影響されるため、同一建築
物でも又同一ALCパネル内においても様々である。し
かし、施工後のALCは必ず炭酸ガスを含む空気と接す
る面があるため、ALC建築廃材中のトバモライトは少
なくとも一部が必ず炭酸化を受けている。[0012] The rate of carbonation of tobermorite in ALC building waste depends not only on the concentration of carbon dioxide gas but also on the relative humidity, temperature, ALC water content, treatment condition of ALC surface (type of coating, thickness, repair), etc. Because they are affected, they vary within the same building and within the same ALC panel. However, since ALC after construction always has a surface in contact with air containing carbon dioxide gas, at least a part of tobermorite in ALC building waste is always carbonated.
【0013】従来からALC工場内で再利用されている
工場内廃材も空気と接するが、再利用されるまでの時間
が数時間程度と極めて短いため、実質上炭酸化を受けて
いない。炭酸化を受けていないトバモライトは、前記特
開平5−319876号公報では、800℃以上に加熱
することでワラストナイト及びゾノライトと呼ばれる鉱
物に変化することが示されている。しかし、本発明者ら
の研究によれば、この場合ゾノライトは生成しないこと
が分かった。これに関しては、文献からも裏付けられて
おり、例えば「水熱化学ハンドブック」技報堂出版の2
98頁には、ゾノライトが800℃ではワラスナイト
(ケイ灰石)に分解すること、同302頁には珪酸イオ
ンの縮合形式が2重鎖の場合(トバモライトがこれに相
当する)はワラスナイトに分解することが記載されてい
る。Although the in-plant waste that has been reused in the ALC factory has come into contact with air, the time until the reuse is extremely short, about several hours, so that it has not substantially undergone carbonation. In Japanese Unexamined Patent Publication No. Hei 5-319876, it is shown that tobermorite that has not been subjected to carbonation changes into minerals called wollastonite and zonolite when heated to 800 ° C. or more. However, according to the study of the present inventors, it was found that zonolite was not formed in this case. This is supported by the literature, for example, “Hydrothermal Chemistry Handbook” published by Gihodo 2
On page 98, the zonolite decomposes into wollastonite (wollastonite) at 800 ° C, and on page 302, when the condensation form of silicate ions is a double chain (tobermorite is equivalent to this), it decomposes into wollastonite. It is described.
【0014】一方、ALC建築廃材中の炭酸化を受けた
トバモライトは、上記のごとく炭酸カルシウムとシリカ
ゲルに分解しているため、本発明により600℃以上に
加熱処理することで、炭酸カルシウムが脱炭酸して酸化
カルシウム(CaO)に変化する。この酸化カルシウム
は水と接触すると水和発熱し、消石灰に変化し得る。同
時に、ALC建築廃材中の炭酸化を受けていない一部の
トバモライトは、600℃以上でその結晶水の一部が離
脱した不安定な結晶に変化する。On the other hand, since carbonated tobermorite in ALC building waste is decomposed into calcium carbonate and silica gel as described above, the calcium carbonate is decarbonated by heat treatment at 600 ° C. or more according to the present invention. To calcium oxide (CaO). When this calcium oxide comes in contact with water, it generates hydration heat and can be changed to slaked lime. At the same time, some non-carbonated tobermorite in ALC building waste is converted into unstable crystals from which a part of the crystallization water is removed at 600 ° C. or higher.
【0015】また、800℃以上では炭酸化していない
トバモライトはワラスナイトに変化するが、工場内廃材
と異なり、炭酸化を受けたALC建築廃材を800℃以
上で焼成した場合、ワラスナイトの結晶性が低く、結晶
構造が完全に一致しない不安定なものが生成することが
分かった。これは、一部分でも炭酸化を受けたトバモラ
イトは、その構造も変化していることを示唆するもので
ある。従って、炭酸化を受けたトバモライトが800℃
以上で分解して生成する鉱物は、不安定なもの、言い換
えると反応しやすいものであることが分かった。At 800 ° C. or higher, non-carbonated tobermorite turns into walathite, but unlike factory waste, when carbonized ALC building waste is fired at 800 ° C. or higher, the crystallinity of walathite is low. It has been found that an unstable substance whose crystal structure does not completely match is formed. This suggests that the structure of tobermorite, which has been partially carbonated, has also changed. Therefore, carbonated tobermorite has a temperature of 800 ° C.
It was found that the minerals generated by the above decomposition were unstable, in other words, those that easily reacted.
【0016】即ち、本発明においては、トバモライトが
一部炭酸化したALC建築廃材を600℃以上で焼成す
ることによって、酸化カルシウムと、トバモライトの一
部が分解した化学的に不安定な珪酸カルシウム系鉱物と
を含み、更に未反応の珪石などを含む、新規な珪酸カル
シウム系原料を得ることができる。That is, in the present invention, by sintering at a temperature of 600 ° C. or more, ALC building waste partially carbonated with tobermorite, calcium oxide and a chemically unstable calcium silicate system in which tobermorite is partially decomposed are used. A novel calcium silicate-based raw material containing minerals and further containing unreacted silica stone can be obtained.
【0017】従って、本発明による珪酸カルシウム系原
料は水と反応し、生石灰が消石灰に水和すると同時に、
結晶性が低く化学的に不安定な珪酸カルシウム系鉱物が
水和して、珪酸カルシウム系水和物を生成することによ
り、硬化するという性質を持っている。つまり、本発明
により、一般に使用されるセメントと同様に、水硬性を
持つ新規な珪酸カルシウム系原料が提供される。Accordingly, the calcium silicate-based raw material according to the present invention reacts with water, and at the same time as quicklime hydrates into slaked lime,
Calcium silicate-based minerals having low crystallinity and being chemically unstable hydrate to form calcium silicate-based hydrates, and thus have the property of hardening. That is, according to the present invention, a novel calcium silicate-based raw material having hydraulic properties is provided in the same manner as a commonly used cement.
【0018】加熱温度については、炭酸カルシウムが分
解される600℃以上から1500℃以下が好ましい。
1500℃を越えると、加熱に対するエネルギーコスト
がかさむのみならず、ALC中の鉱物粒子が溶融し、比
表面積が小さくなると同時に、結晶性の高い珪酸カルシ
ウム系鉱物が固相反応で生成する可能性もあり、水和反
応性に乏しくなるためである。尚、加熱のための熱源と
しては、ゴミ焼却場の廃熱を利用することも可能であ
る。The heating temperature is preferably from 600 ° C. to 1500 ° C. at which calcium carbonate is decomposed.
When the temperature exceeds 1500 ° C., not only does the energy cost for heating increase, but also the mineral particles in the ALC melt and the specific surface area decreases, and at the same time, the possibility that calcium silicate-based minerals with high crystallinity are generated by the solid-phase reaction is increased. This is because the hydration reactivity becomes poor. In addition, as a heat source for heating, waste heat of a garbage incineration plant can be used.
【0019】本発明による珪酸カルシウム系原料は、そ
れ自身で水硬性を有するため、一般のポルトランドセメ
ントなどに混合して使用することにより、セメント使用
量の削減を図ることができる。また、地盤改良材として
用いれば、その水硬性により、単にALC廃材を埋立て
て使用した場合よりも、地盤強度が増すことが期待され
る。Since the calcium silicate-based raw material according to the present invention has hydraulic properties by itself, it is possible to reduce the amount of cement used by mixing it with ordinary Portland cement or the like. In addition, when used as a ground improvement material, it is expected that the ground strength will be increased due to its hydraulic property as compared with a case where the ALC waste material is simply buried and used.
【0020】[0020]
【実施例】建築物の解体現場から炭酸化したALC建築
廃材を回収し、そのままパネルごと電気炉に入れ、下記
表1に示す各温度で2時間焼成した。ALC廃材のパネ
ル表面の塗装材は残したまま加熱処理したが、塗料は熱
分解して収縮し、容易に剥離することができた。その
後、焼成物を粒径150μm以下に粉砕して、珪酸カル
シウム系原料とした。尚、各ALC廃材に関する炭酸化
の有無は、X線回析により、Cukα2θ=36.9°
付近のカルサイト又はCukα2θ=32.7°付近の
カルサイトのピークの有無により測定した。EXAMPLE A carbonized ALC building waste was collected from a building demolition site, placed in an electric furnace with the panel as it was, and fired at each temperature shown in Table 1 below for 2 hours. Although heat treatment was performed while leaving the coating material on the panel surface of the ALC waste material, the coating material was thermally decomposed and shrunk, and could be easily peeled off. Thereafter, the fired product was pulverized to a particle size of 150 μm or less to obtain a calcium silicate-based raw material. The presence or absence of carbonation of each ALC waste material was determined by X-ray diffraction using Cu k α2θ = 36.9 °.
The measurement was performed based on the presence or absence of a peak of calcite in the vicinity or a calcite near Cu k α2θ = 32.7 °.
【0021】得られた各珪酸カルシウム系原料を普通ポ
ルトランドセメントの10重量%又は50重量%と置換
して、通常のモルタルを作製し、その28日圧縮強度を
JIS R5201に従って測定した。尚、モルタルの
配合は、全ての試料で、普通ポルトランドセメントと珪
酸カルシウム系原料の合計520gに、標準砂1040
g、水338gとした。比較のために、ALC製造工場
内で発生した炭酸化していない工場内廃材を焼成して添
加した試料1及び試料2、並びにALC廃材を何ら添加
しない試料15についても、同様に圧縮強度を測定し
た。得られた結果を下記表1に示した。Each of the obtained calcium silicate-based raw materials was replaced with 10% by weight or 50% by weight of ordinary Portland cement to prepare a normal mortar, and its 28-day compressive strength was measured according to JIS R5201. The mortar was mixed in all samples in a total of 520 g of ordinary Portland cement and calcium silicate-based raw materials, and standard sand 1040.
g of water and 338 g of water. For comparison, the compressive strength was similarly measured for Samples 1 and 2 obtained by calcining and adding non-carbonated in-plant waste generated in the ALC manufacturing plant and Sample 15 to which no ALC waste was added. . The results obtained are shown in Table 1 below.
【0022】[0022]
【表1】 (注)表中の*を付した試料は比較例である。[Table 1] (Note) Samples marked with * in the table are comparative examples.
【0023】上記表1から分かるように、ALCの工場
内廃材を焼成して添加した試料1及び試料2では、AL
C廃材無添加の試料15(通常のモルタル)に比べ、モ
ルタルの圧縮強度が大幅に低下している。また、ALC
建築廃材を本発明範囲外の温度で焼成して添加した試料
3及び試料14でも、モルタルの圧縮強度が無添加の試
料15よりも大幅に低下している。As can be seen from Table 1 above, in samples 1 and 2 in which the waste material in the ALC factory was calcined and added, AL
The compressive strength of the mortar is significantly lower than that of Sample 15 (normal mortar) without the addition of C waste material. Also, ALC
Also in Samples 3 and 14 in which the building waste was fired at a temperature outside the range of the present invention and added, the compressive strength of the mortar was much lower than that of Sample 15 without addition.
【0024】一方、珪酸カルシウム系原料をポルトラン
ドセメントの一部と置換してモルタルに添加した本発明
の試料4〜13では、ALC廃材無添加の試料15に比
べ、モルタルの圧縮強度は若干低下しているものの、従
来例の試料1及び試料2に比べると強度が向上している
ことが分かる。即ち、本発明による珪酸カルシウム系原
料は、ポルトランドセメントと同様に水硬性を発揮する
のみならず、ポルトランドセメントの硬化性能を向上さ
せる効果を有するものである。On the other hand, in the samples 4 to 13 of the present invention in which the calcium silicate-based raw material was replaced with a part of Portland cement and added to the mortar, the compressive strength of the mortar was slightly lower than that of the sample 15 without the ALC waste material. However, it can be seen that the strength is improved as compared with Samples 1 and 2 of the conventional example. That is, the calcium silicate-based raw material according to the present invention not only exhibits hydraulic property like Portland cement but also has an effect of improving the hardening performance of Portland cement.
【0025】[0025]
【発明の効果】本発明によれば、建築物の解体現場から
発生するALC建築廃材を再利用して、セメントの代替
原料として使用できる珪酸カルシム水硬性原料を提供す
ることができ、産業廃棄物の削減に寄与するのみなら
ず、枯渇しつつある天然原料の省資源化にも有効であ
る。According to the present invention, it is possible to provide a calcium silicate hydraulic raw material that can be used as a substitute material for cement by recycling ALC building waste generated from a building demolition site, and to provide industrial waste. Not only does it contribute to the reduction of natural resources, but it is also effective in saving resources of depleting natural raw materials.
Claims (2)
加熱処理して得られたものであり、酸化カルシウムと、
トバモライトの一部が分解した珪酸カルシウム系鉱物と
を含むことを特徴とする水硬性珪酸カルシウム系原料。1. An ALC building waste obtained by heat treatment at 600 to 1500 ° C., comprising calcium oxide,
A hydraulic calcium silicate-based raw material comprising a part of tobermorite decomposed with a calcium silicate-based mineral.
C建築廃材を、600〜1500℃で加熱処理すること
を特徴とする水硬性珪酸カルシウム系原料の製造方法。2. AL in which a part of tobermorite is carbonated
C. A method for producing a hydraulic calcium silicate-based raw material, wherein a waste construction material is heat-treated at 600 to 1500 ° C.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000006027A JP2001199750A (en) | 2000-01-11 | 2000-01-11 | Hydraulic calcium silicate-based raw material using ALC building waste and method for producing the same |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000006027A JP2001199750A (en) | 2000-01-11 | 2000-01-11 | Hydraulic calcium silicate-based raw material using ALC building waste and method for producing the same |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2001199750A true JP2001199750A (en) | 2001-07-24 |
Family
ID=18534618
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2000006027A Pending JP2001199750A (en) | 2000-01-11 | 2000-01-11 | Hydraulic calcium silicate-based raw material using ALC building waste and method for producing the same |
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| Country | Link |
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| JP (1) | JP2001199750A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR101709603B1 (en) * | 2016-06-24 | 2017-02-23 | 주식회사 합동종합건설 | Mortar Comprising the Surface Compacting Admixture to Repair Underwater Concrete Structure and Underwater Repairing Method of Concrete Structure Therewith |
-
2000
- 2000-01-11 JP JP2000006027A patent/JP2001199750A/en active Pending
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR101709603B1 (en) * | 2016-06-24 | 2017-02-23 | 주식회사 합동종합건설 | Mortar Comprising the Surface Compacting Admixture to Repair Underwater Concrete Structure and Underwater Repairing Method of Concrete Structure Therewith |
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