JPH06106153A - Cement solidification of incineration ash and cement solidified product of incineration ash - Google Patents

Cement solidification of incineration ash and cement solidified product of incineration ash

Info

Publication number
JPH06106153A
JPH06106153A JP26189692A JP26189692A JPH06106153A JP H06106153 A JPH06106153 A JP H06106153A JP 26189692 A JP26189692 A JP 26189692A JP 26189692 A JP26189692 A JP 26189692A JP H06106153 A JPH06106153 A JP H06106153A
Authority
JP
Japan
Prior art keywords
cement
water
incineration ash
ash
incinerated ash
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.)
Withdrawn
Application number
JP26189692A
Other languages
Japanese (ja)
Inventor
Ikou Shino
医晃 示野
Takashi Tanioka
隆 谷岡
Akiyoshi Yamane
朗義 山根
Saburo Sawada
三郎 沢田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kobe Steel Ltd
Original Assignee
Kobe Steel Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Kobe Steel Ltd filed Critical Kobe Steel Ltd
Priority to JP26189692A priority Critical patent/JPH06106153A/en
Publication of JPH06106153A publication Critical patent/JPH06106153A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/02Compositions 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
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2103/00Function or property of ingredients for mortars, concrete or artificial stone
    • C04B2103/0045Polymers chosen for their physico-chemical characteristics
    • C04B2103/0051Water-absorbing polymers, hydrophilic polymers
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00017Aspects relating to the protection of the environment
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)
  • Curing Cements, Concrete, And Artificial Stone (AREA)

Abstract

PURPOSE:To produce a cement solidified product of incineration ash utilizable as resources, in producing the cement solidified product using incineration ash, by suppressing the elution of a harmful substance and enhancing the strength of the cement solidified product to a large extent. CONSTITUTION:A raw material containing the incineration ash of waste refuse or sewage sludge, cement, aggrigate and a water absorbable polymer having absorbed water is kneaded to prepare paste accelerated in initial hydration and this paste is molded. Pref., the raw material consisting of 100 pts.wt. of incineration ash, 65 pts.wt. or more of cement, 50 pts.wt. or more of aggregate and 0.5 pts.wt. or more of a water absorbable polymer (at the time of drying) and containing 25-45wt.% of water with respect to the sum amt. of incineration ash and cement is used.

Description

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

【0001】[0001]

【産業上の利用分野】本発明はごみや下水汚泥等を焼却
することによって生成する焼却灰をセメントで固化させ
る方法に関し、詳細には低水セメント比で、有害物質を
溶出することなく、高強度なセメント固化品を得ること
ができる焼却灰の処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for solidifying incineration ash produced by incinerating garbage, sewage sludge and the like with cement, and more specifically, it has a low water cement ratio and does not elute harmful substances, The present invention relates to a method for treating incinerated ash that can obtain a solidified cement product.

【0002】[0002]

【従来の技術】都市から産出されるごみや下水汚泥が年
々増加しているが、これらのごみや下水汚泥を焼却した
後にできる焼却灰については、埋立地確保の問題、含ま
れている有毒重金属の溶出の問題があり、焼却灰の安定
化、減容化、資源化等の技術開発が進められている。例
えば、財団法人廃棄物研究財団によって行なわれた「灰
の安定化等処理技術開発プロジェクト」では、焼却灰を
セメントで固化する方法について詳しく検討されている
(同プロジェクト 平成元年度報告書)。
2. Description of the Related Art The amount of garbage and sewage sludge produced from cities has been increasing year by year. Regarding the incineration ash produced after incinerating such garbage and sewage sludge, the problem of securing landfill sites, the toxic heavy metals contained There is a problem of elution of ash, and technological developments such as stabilization, volume reduction, and resource recovery of incinerated ash are underway. For example, in the "Technology development project for stabilization of ash" conducted by the Waste Research Foundation, a method of solidifying incinerated ash with cement is being examined in detail (the project 1989 report).

【0003】上記報告書中には、セメント:焼却灰=1
5〜60:100、水:セメント=110〜570:1
00(水:焼却灰+セメント=24〜119:100)
等の配合比(重量比)の原料をオムニミキサー等で混合
した後、押出し成形またはプレス成形法でブロック状等
にセメント固化し、重金属等の有害成分の溶出テストや
強度測定を行なっている。この実験方法では、焼却灰が
水硬性に乏しいのにセメント量は15〜60(対焼却
灰)と少なく、加圧成形させるために大量の水分を添加
している。しかし、セメントの水和反応に必要な理論水
分量は水セメント比で25%前後であることから、上記
実験では大部分の水分が固化反応に寄与できない余剰水
分となって蒸発することになるので、ボイドが多く発生
し、比表面積の増大、ひいては重金属有毒成分の溶出増
大や、成形品強度の低下を引き起こしており、実際に使
用可能な強度を有し、かつ安全なセメント固化品は得ら
れていない。
In the above report, cement: incineration ash = 1
5-60: 100, Water: Cement = 110-570: 1
00 (water: incineration ash + cement = 24-119: 100)
After mixing raw materials with a mixing ratio (weight ratio) such as the above with an omni mixer or the like, the mixture is cemented into a block shape by extrusion molding or press molding, and the elution test and the strength measurement of harmful components such as heavy metals are performed. In this experimental method, the amount of cement is as small as 15 to 60 (against incineration ash), although the incineration ash has poor hydraulic properties, and a large amount of water is added for pressure molding. However, since the theoretical amount of water required for the hydration reaction of cement is around 25% in water-cement ratio, most of the water will evaporate as excess water that cannot contribute to the solidification reaction in the above experiment. In addition, many voids are generated, the specific surface area is increased, the elution of toxic components of heavy metals is increased, and the strength of molded products is decreased.Therefore, it is possible to obtain a cement-solidified product that has practically usable strength and is safe. Not not.

【0004】一方、焼却灰を熱プラズマ溶融炉で溶融さ
せる方法も検討されているが、設備が大型化・複雑化
し、また大量のエネルギーを使うために一般的ではな
い。さらに、焼却灰を粘土等の一部代替として使用し、
焼結させて透水タイルを製造する方法が検討されている
が、焼結の際に焼却灰中の低融点有毒物質が揮発する問
題があると共に、やはり大量のエネルギーを使うため資
源化という観点からはデメリットの方が大きいのが現状
である。
On the other hand, a method of melting incinerated ash in a thermal plasma melting furnace has been studied, but it is not general because the equipment becomes large and complicated and a large amount of energy is used. Furthermore, using incineration ash as a partial substitute for clay,
A method for producing a permeable tile by sintering has been studied, but there is a problem that the low melting point toxic substance in the incineration ash volatilizes during sintering, and since a large amount of energy is used, it is also considered as a resource. At present, the disadvantage is greater.

【0005】[0005]

【発明が解決しようとする課題】本発明は上記事情に着
目してなされたものであって、焼却灰を使用してセメン
ト固化品を製造するに当たり、有毒物質の溶出を抑える
ことと、成形固化品の強度を大幅に向上させることによ
って、資源として利用可能な焼却灰のセメント固化品を
製造することを目的とする。
SUMMARY OF THE INVENTION The present invention has been made in view of the above circumstances, and suppresses elution of toxic substances when forming cement-solidified products using incinerated ash, and solidifies by molding. The purpose of the present invention is to produce a cement-solidified product of incinerated ash that can be used as a resource by significantly improving the strength of the product.

【0006】[0006]

【課題を解決するための手段】上記目的を達成すること
ができた本発明の焼却灰のセメント固化方法とは、ごみ
・下水汚泥等の焼却灰、セメント、骨材、水を吸収した
吸水性ポリマーを含む原料を混練して初期水和が促進さ
れたペースト状にした後に成形を行なうことを要旨とす
る。好ましい原料の配合比は、焼却灰100重量部に対
してセメント:65重量部以上、骨材:50重量部以
上、吸水性ポリマー(乾燥時):0.5重量部以上、
水:焼却灰とセメントの合計量の25〜45重量%であ
り、本方法を用いて固化された焼却灰のセメント固化品
も本発明に包含される。
[Means for Solving the Problems] The cement solidification method of incineration ash of the present invention which has achieved the above-mentioned object is a water-absorptive material that absorbs incineration ash such as dust and sewage sludge, cement, aggregate and water. The gist is that the raw material containing a polymer is kneaded to form a paste in which initial hydration is promoted, and then the molding is performed. The preferable mixing ratio of raw materials is 100 parts by weight of incinerated ash, 65 parts by weight or more of cement, 50 parts by weight or more of aggregate, and 0.5% by weight or more of water-absorbing polymer (dry).
Water: 25 to 45% by weight of the total amount of incinerated ash and cement, and a cement-solidified product of incinerated ash solidified by using the present method is also included in the present invention.

【0007】[0007]

【作用】本発明者らは、水硬性に乏しい焼却灰を資源と
して使用可能な強度を持つ固化品とするために検討した
結果、 水セメント比を極力減らすために吸水性ポリマーを使
用する。 焼却灰に対するセメント量は65重量部以上が強度発
現には好ましい。 原料を混合するときには、圧縮や剪断作用による練り
効果の高いミキサーを用いることが、初期水和促進のた
めに好ましい。 等の点を明らかにし、本発明に至ったものである。以下
詳細に説明する。
The present inventors have studied to make incinerated ash having poor hydraulic properties into a solidified product having a strength that can be used as a resource, and as a result, use a water-absorbing polymer to reduce the water-cement ratio as much as possible. The amount of cement with respect to the incinerated ash is preferably 65 parts by weight or more for strength development. When mixing the raw materials, it is preferable to use a mixer having a high kneading effect due to compression or shearing action, in order to promote initial hydration. The present invention has been accomplished by clarifying the above points. The details will be described below.

【0008】本発明において、焼却灰とは一般的に都市
で廃棄されるごみや、下水中の汚泥等を焼却した後に得
られる灰あるいは、火力発電所によって産出される石炭
灰等である。都市ごみ焼却灰は下水汚泥焼却灰や石炭灰
に比べて灰の粒径が一般的に大きいので、セメント固化
品の緻密性を向上させるには、都市ごみ焼却灰と、下水
汚泥焼却灰・石炭灰を適宜混合して使用する方が最密充
填効果が得られて好ましい。
In the present invention, the incineration ash is generally trash obtained in the city, ash obtained after incinerating sludge in sewage, or coal ash produced by a thermal power plant. Municipal solid waste incineration ash generally has a larger ash particle size than sewage sludge incineration ash and coal ash. Therefore, in order to improve the compactness of cement solidified products, municipal solid waste incineration ash and sewage sludge incineration ash / coal can be improved. It is preferable to use a mixture of ash as appropriate because the closest packing effect can be obtained.

【0009】この焼却灰は、セメント、骨材、水を吸収
した吸水性ポリマーと共に混練されてペースト状とされ
る。原料ペーストの作成方法としては、吸水性ポリマー
に所定量の水を吸収させたものと、焼却灰、骨材、そし
て充分量のセメントと共に万能混合機、ニーダ、強制練
りミキサー等の練り効果の高いミキサーで混練すれば良
い。
This incinerated ash is kneaded together with cement, aggregate and water-absorbing polymer that has absorbed water to form a paste. As a method for preparing the raw material paste, a water-absorbing polymer having absorbed a predetermined amount of water, incineration ash, aggregate, and a sufficient amount of cement together with a universal mixer, kneader, forced kneading mixer, etc. have a high kneading effect. Knead with a mixer.

【0010】水を吸収した吸水性ポリマーは粉体状態で
あるので、最初は焼却灰、骨材、セメント粒子、ポリマ
ー粒子が粉体のまま非常に良好に分散する。また、圧縮
応力や剪断応力によって焼却灰粒子やセメント粒子中の
造粒物や凝集物が破壊される。特に下水汚泥焼却灰のよ
うな粒径の小さな灰は吸湿等によって造粒しやすいが、
振り混ぜ中心のオムニミキサーではこの造粒を粉砕する
ことはできないため、練り効果の高いミキサーで混練す
べきである。造粒物が残存していると均一な固化品が得
られず、強度低下、有毒成分溶出の要因となり好ましく
ない。
Since the water-absorbing polymer that has absorbed water is in a powder state, initially the incinerated ash, aggregate, cement particles and polymer particles are very well dispersed as a powder. In addition, granules and aggregates in the incinerated ash particles and cement particles are destroyed by the compressive stress and the shear stress. In particular, ash with a small particle size, such as sewage sludge incineration ash, is easy to granulate due to moisture absorption, etc.
Since this granulation cannot be crushed with an omni mixer, which is mainly a shaking mixer, it should be kneaded with a mixer having a high kneading effect. If the granulated product remains, a uniform solidified product cannot be obtained, which is not preferable because it causes strength reduction and elution of toxic components.

【0011】良好かつ均一に分散した焼却灰、骨材、セ
メント粒子、ポリマー粒子のうち、セメント粒子と吸水
ポリマー粒子が接触することによって、セメント粒子の
アルカリイオンの影響でポリマー粒子が放水を始める。
吸水したポリマーは圧力だけでは放水しにくく、アルカ
リイオンの存在によって水を離すためである。混練によ
ってポリマー粒子表面のイオン平衡状態が破壊され、さ
らに放水が促進されるため、短時間にセメント粒子は水
に充分に濡れることができ、この濡れたセメントによっ
て焼却灰も簡単にペースト状になるのである。なお、本
発明法によれば練り効果の高いミキサーを用いるために
ポリマー粒子の放水は素早く行なわれるので、造粒物の
多い焼却灰を使う時などはポリマー粒子の添加時期を少
し遅らせて、粉体状のままで混練をしばらく行なうこと
も効果的である。
Among the incinerated ash, aggregate, cement particles, and polymer particles that are well and uniformly dispersed, the cement particles and the water-absorbing polymer particles come into contact with each other, so that the polymer particles start water discharge under the influence of the alkali ions of the cement particles.
This is because the water-absorbed polymer is difficult to release water only by pressure and releases water due to the presence of alkali ions. The ionic equilibrium state on the surface of polymer particles is destroyed by kneading, and water discharge is further promoted, so that cement particles can be sufficiently wetted with water in a short time, and the incinerated ash can be easily made into a paste by this wet cement. Of. In addition, according to the method of the present invention, since the polymer particles are discharged quickly because a mixer having a high kneading effect is used, when the incinerated ash with many granules is used, the addition time of the polymer particles is delayed a little, It is also effective to carry out kneading for a while in a physical condition.

【0012】セメント粒子が水に濡れると水和反応が開
始される。セメント粒子とポリマー粒子、および焼却
灰、骨材は均一に分散しているため、系全体的に水和反
応が進行していく。このため水和物に生成に伴って原料
ペーストはより緻密になり、最終的に得られるセメント
固化品が高強度となるのである。オムニミキサーで振り
混ぜているだけの従来法では、上述のような本発明にお
ける初期水和促進といった長所を享受することはできな
い。従って従来法では成形は粉体の締め固めとなって内
部の空隙が多くなり、強度の低い固化品しか得られな
い。
When the cement particles get wet with water, a hydration reaction is started. Since the cement particles and the polymer particles, the incinerated ash, and the aggregate are uniformly dispersed, the hydration reaction proceeds throughout the system. For this reason, the raw material paste becomes more dense as the hydrate is formed, and the finally solidified cement product has high strength. The conventional method of simply shaking the mixture with an omni mixer cannot enjoy the advantages of promoting the initial hydration in the present invention as described above. Therefore, in the conventional method, the powder is compacted in the conventional method to increase the internal voids, and only a solidified product having low strength can be obtained.

【0013】本発明で用いられる吸水性ポリマーとして
は、最大吸水能が50〜300倍(対乾燥ポリマー重
量)程度のものであればその素材は特に限定されない
が、吸水後も独立粒状形態を保つ特徴を持つものが好ま
しく使用される。吸水性ポリマーに吸水させる水の量
(水・吸水性ポリマー比)は、ポリマー乾燥重量に対し
て30〜200倍が好ましい。吸水量が30倍より小さ
いと、強アルカリ状態であっても放水が短時間で行なわ
れず、10倍程度の水がポリマー中に残存してしまい、
セメントを充分に水和させることができない。一方吸水
量が200倍を超えると、ポリマー表面の付着水が多大
となって、水中にポリマーが浮遊するような形態となる
ために粉体として取り扱うことが困難となり、原料ペー
スト作成時に均一に混合できなくなる。吸水ポリマーの
使用量はこの吸水倍率と後述の必要水分量によって適宜
選択される。一般的には乾燥重量で0.5重量部以上使
用される。
The water-absorbing polymer used in the present invention is not particularly limited as long as it has a maximum water absorption capacity of about 50 to 300 times (based on the dry polymer weight), but it maintains an independent granular form even after water absorption. Those having characteristics are preferably used. The amount of water absorbed by the water-absorbent polymer (water / water-absorbent polymer ratio) is preferably 30 to 200 times the polymer dry weight. If the amount of water absorption is less than 30 times, water is not discharged in a short time even in a strong alkaline state, and about 10 times as much water remains in the polymer,
The cement cannot be fully hydrated. On the other hand, if the water absorption exceeds 200 times, the amount of water adhering to the surface of the polymer will be so large that the polymer will be suspended in water, making it difficult to handle as a powder, and evenly mixing when preparing the raw material paste. become unable. The amount of the water-absorbing polymer used is appropriately selected depending on this water absorption capacity and the necessary amount of water described later. Generally, it is used in a dry weight of 0.5 parts by weight or more.

【0014】吸水性ポリマーに吸収させる水の量は、焼
却灰とセメントの合計量に対して25〜45重量%が好
ましい範囲である。セメントの水和反応に必要な水分理
論量はセメントに対して25重量%程度であるので、焼
却灰の分だけ若干過剰ではあるが、焼却灰中でもわずか
に水和反応が起こって、水和物を生成するため本発明の
低水分量では余剰水分は問題となり得ない。焼却灰をセ
メントペースト中に取りこんで緻密な固化品を製造する
ためには上記の水分量が最適である。
The amount of water absorbed by the water-absorbent polymer is preferably in the range of 25 to 45% by weight based on the total amount of incinerated ash and cement. Since the theoretical amount of water required for the hydration reaction of cement is about 25% by weight with respect to the cement, it is slightly excessive by the amount of incinerated ash, but a slight hydration reaction also occurs in the incinerated ash, resulting in a hydrate. Therefore, excess water cannot be a problem with the low water content of the present invention. The above water content is optimal for incorporating incinerated ash into cement paste to produce a dense solidified product.

【0015】水の量が焼却灰とセメントの合計量の25
重量%より少ないと、特に汚泥焼却灰のような粒径の小
さな灰は比表面積が大きいので必要水分量が多くなるた
め、セメントペーストの中に灰を完全に取り込むことが
むずかしくなる。また、水量が45重量%より大きくな
ると、特に都市ごみ焼却灰のように粒径の大きな灰では
上記と逆に必要水分量が少なくなるので、余剰水分が多
くなって好ましくない。例えば前述の従来例では水セメ
ント比110%以上もの大量な水を加えているので、加
圧成形時に有毒成分を溶解した水が放出されて水処理が
必要となったり、成形品にボイドが発生し、このボイド
から有毒成分が溶出したり、強度が低下する等の不都合
を生じる。
The amount of water is 25% of the total amount of incinerated ash and cement.
If the content is less than wt%, especially the ash having a small particle size such as sludge incineration ash has a large specific surface area and thus the required water content is large, so that it is difficult to completely incorporate the ash into the cement paste. On the other hand, if the amount of water is more than 45% by weight, the amount of water required for ash having a large particle size, such as incineration ash of municipal solid waste, is small, which is contrary to the above. For example, in the above-mentioned conventional example, a large amount of water having a water-cement ratio of 110% or more is added, so that water in which toxic components are dissolved is released during pressure molding and water treatment is required, or a void is generated in a molded product. However, this causes inconveniences such as the toxic components being eluted from the voids and the strength being lowered.

【0016】本発明において用いられるセメントは、焼
却灰を固め、有毒成分である重金属が溶出できないよう
に働くマトリクス材料である。本発明では特にセメント
の種類は限定されず、ポルトランドセメント、白色セメ
ント、スラグセメント、アルミナセメント等一般に用い
られるセメントが適用できる。セメント量は、焼却灰1
00重量部に対し、65重量部以上必要である。65重
量部より少ないと、焼却灰表面をセメントペーストで充
分に濡らせないため、緻密な成形品が得られず、有害成
分をセメントで固定できなくなる。
The cement used in the present invention is a matrix material which hardens incinerated ash and prevents heavy metals, which are toxic components, from eluting. In the present invention, the type of cement is not particularly limited, and commonly used cement such as Portland cement, white cement, slag cement, and alumina cement can be applied. The amount of cement is incinerated ash 1
It is necessary to use 65 parts by weight or more with respect to 00 parts by weight. If the amount is less than 65 parts by weight, the surface of the incinerated ash cannot be sufficiently wetted with the cement paste, so that a dense molded product cannot be obtained and the harmful components cannot be fixed with cement.

【0017】骨材としては安山岩等の砕石や硅砂、無機
質の微粉末充填剤等が例示でき、焼却灰100重量部に
対する骨材の使用量は50重量部以上が好ましい。骨材
使用量が50重量部より少ないと、セメントの水和によ
る収縮を骨材でカバーすることができなくなるため成形
品にクラックが発生することがある。
Examples of the aggregate include crushed stones such as andesite, silica sand, and an inorganic fine powder filler, and the amount of the aggregate used is preferably 50 parts by weight or more with respect to 100 parts by weight of incinerated ash. If the amount of aggregate used is less than 50 parts by weight, the aggregate cannot cover shrinkage due to hydration of cement, and thus cracks may occur in the molded product.

【0018】本発明では、混練後のペーストを公知の加
圧成形、押し出し成形、打設・流し込み等の方法で固化
成形させることによって緻密でかつ高強度、また有毒成
分の溶出のない実用性に優れた焼却灰のセメント固化品
を得ることができる。この時賦形に用いる型枠や金型表
面を滑らかな鏡面仕様とすれば、ぺースト状の原料が余
剰水の脱離による収縮のない状態で緻密しながら固化し
ていくために、表面光沢に優れた固化品を得ることが可
能である。従って従来の埋め立てのみにしか使用できな
かったセメント固化品を、タイルやインターブロッキン
グブロック等に使用することができ、更に資源活用の範
囲が広がるものである。
In the present invention, the paste after kneading is solidified and molded by a known method such as pressure molding, extrusion molding, casting / casting, etc., so that the paste is compact and has high strength and practical use without toxic component elution. An excellent cement-solidified product of incinerated ash can be obtained. If the mold used for this shaping and the surface of the mold have a smooth mirror surface specification, the paste-like raw material will solidify while compacting without shrinkage due to desorption of excess water, so that the surface gloss It is possible to obtain an excellent solidified product. Therefore, the cement-solidified product which can be used only for conventional landfill can be used for tiles, interblocking blocks, etc., and the range of resource utilization is further expanded.

【0019】[0019]

【実施例】以下に実施例を挙げて、本発明をより具体的
に説明するが、下記実施例は本発明を制限するものでは
なく、前・後記の趣旨を逸脱しない範囲で変更実施する
ことは全て本発明の技術範囲に包含される。尚、
「部」、「%」とあるのは特にこだわらない限り「重量
部」、「重量%」を示す。
EXAMPLES The present invention will be described in more detail with reference to the following examples, but the following examples do not limit the present invention, and various modifications may be made without departing from the spirit of the above and the following. Are all included in the technical scope of the present invention. still,
Unless otherwise specified, "part" and "%" mean "part by weight" and "% by weight", respectively.

【0020】実施例1 材料:都市ごみ焼却灰 100重量部 ポルトランドセメント 150 〃(セメント/焼却灰=150 %) 骨材(5号珪砂) 100 〃 水 75 〃(水/セメント=50%; 水/(セメント+焼却灰)=30%) 吸水性ポリマー 0.75 〃 [大阪有機化学工業(株)製BL-100;粒径70〜100 μm;100 倍吸水] Example 1 Material: 100% by weight of municipal waste incinerated ash Portland cement 150 〃 (cement / incinerated ash = 150%) Aggregate (No. 5 silica sand) 100 〃 Water 75 〃 (water / cement = 50%; water / (Cement + Incinerated ash) = 30%) Water-absorbent polymer 0.75 〃 [Osaka Organic Chemical Industry Co., Ltd. BL-100; particle size 70-100 µm; 100 times water absorption]

【0021】上記材料のうち、水(水道水)75部を容器
に入れ、撹拌しながら吸水性ポリマー0.75部を徐々に加
えた。5分間撹拌を続けて吸水させ、撹拌を止め、粉体
状の吸水後のポリマーを得た。他の材料を5リットルの
混練機(株式会社ダルトン製真空式万能撹拌混合機)で
1分間混練した後に粉体状の水を加え、10分間混練を
行なってペースト状の原料を得た。
Of the above materials, 75 parts of water (tap water) was placed in a container, and 0.75 part of a water-absorbent polymer was gradually added with stirring. Stirring was continued for 5 minutes to absorb water, stirring was stopped, and a powdered polymer after water absorption was obtained. Other materials were kneaded with a 5-liter kneader (vacuum universal stirring mixer manufactured by Dalton Co., Ltd.) for 1 minute, and then powdered water was added and kneaded for 10 minutes to obtain a paste-like raw material.

【0022】この原料ペーストをS45C(▽▽仕上げ)の
型材に鉱物油を薄く塗布した金型にチャージして、30kg
f/cm2 の成形圧力で 160mm×40mm×12mmとなるよう10
分間プレス成形した。この成形品を型内に入れたまま室
温で2日間養生した。得られた成形固化品について、曲
げ・試験および全細孔体積および光沢度の測定を行なっ
た。曲げ強度は、材令2日のものをスパン100 mmとし、
インストロン万能試験材で3点曲げた結果であり、細孔
体積は島津ポアライザー9310型を用いて水銀圧入法で求
めた。また光沢度は、ミノルタカメラ製の光沢計GM-060
を用いて測定した。測定結果を表1に示した。
30 kg of this raw material paste is charged into a mold in which mineral oil is thinly applied to a S45C (▽▽ finish) mold material.
10 x 160 mm x 40 mm x 12 mm at a molding pressure of f / cm 2
Press molded for minutes. The molded product was aged at room temperature for 2 days while being kept in the mold. Bending / testing and measurement of total pore volume and gloss were performed on the obtained molded and solidified product. Bending strength is 100 mm in span of 2 days old,
It is the result of 3-point bending with an Instron universal test material, and the pore volume was determined by the mercury injection method using a Shimadzu Poiserizer 9310 type. Also, the glossiness is GM-060, a gloss meter manufactured by Minolta Camera.
Was measured using. The measurement results are shown in Table 1.

【0023】実施例2 金型表面を硬質クロムメッキ・バフ研磨仕上げとした以
外は実施例1と同様に成形・評価した。実施例3 実施例2の条件において、材料配合を次の様に変えた以
外は同様に成形・評価を行なった。
Example 2 Molding and evaluation were carried out in the same manner as in Example 1 except that the mold surface was hard chrome plated and buffed. Example 3 Under the conditions of Example 2, molding and evaluation were performed in the same manner except that the material composition was changed as follows.

【0024】 材料:都市ごみ焼却灰 100 重量部(平均粒径 約 0.1mm) 高分子系汚泥焼却灰 25 〃 (平均粒径 約 4μm) ポルトランドセメント 150 〃 (平均粒径 約 10μm) (セメント/焼却灰= 120%) 骨材(5号珪砂) 100 〃 (平均粒径約 0.5mm) 水 80 〃 (水/セメント=50%, 水/(焼却灰+セメント)=29%) 吸水性ポリマー 0.8 〃 Material: 100 parts by weight of municipal waste incineration ash (average particle size: about 0. 1 mm) Polymer-based sludge incineration ash 25 〃 (average particle size about 4 μm) Portland cement 150 〃 (average particle size about 10 μm) (cement / incineration ash = 120%) Aggregate (No. 5 silica sand) 100 〃 (average particle size About 0. 5mm) Water 80〃 (water / cement = 50%, water / (incineration ash + cement) = 29%) Water-absorbent polymer 0. 8 〃

【0025】比較例 材料:都市ごみ焼却灰 100 重量部 ポルトランドセメント 30 〃(セメント/焼却灰=30%) 水 50 〃(水/セメント=167 %、 水/(焼却灰+セメント)=38%) Comparative Example Material: 100% by weight of municipal waste incinerated ash Portland cement 30 〃 (cement / incinerated ash = 30%) Water 50 〃 (water / cement = 167%, water / (incinerated ash + cement) = 38%)

【0026】上記材料のうち焼却灰とセメントを千代田
技研工業(株)製 オムニミキサーOM−5に入れて3
0秒間撹拌した後に、水を加え120秒撹拌した。3mm
程度に造粒した粉体状の混合物が得られた。この混合物
を、実施例1で用いたものと同様の金型で同条件でプレ
ス成形した。ただし、プレス成形後に金型を分解して即
時脱型し、脱型したまま室温で2日間養生し、評価を行
なった。実施例1〜3および比較例の評価結果を表1に
併記した。また、実施例1と比較例について環境庁公示
第13号試験をもとに重金属の溶出試験を行ない、結果
を表2に示した。
Of the above materials, incinerated ash and cement were placed in an omnimixer OM-5 manufactured by Chiyoda Giken Kogyo Co., Ltd.
After stirring for 0 seconds, water was added and the mixture was stirred for 120 seconds. 3 mm
A powdery mixture was obtained which was granulated to a degree. This mixture was press-molded under the same conditions with the same mold as that used in Example 1. However, after the press molding, the mold was disassembled and immediately released from the mold, and the molded product was aged at room temperature for 2 days for evaluation. The evaluation results of Examples 1 to 3 and Comparative Example are also shown in Table 1. Further, with respect to Example 1 and Comparative Example, a heavy metal dissolution test was carried out based on the Environmental Agency Public Notice No. 13 test, and the results are shown in Table 2.

【0027】[0027]

【表1】 [Table 1]

【0028】[0028]

【表2】 [Table 2]

【0029】表1より、本発明実施例は、全細孔体積が
比較例の1/10以下となっており緻密であるため、曲
げ強度が6〜7倍に向上していることが分かる。また、
金型を鏡面仕上げして成形した実施例2および3はきれ
いな光沢をもつ固化品が得られた。また表2の結果か
ら、本発明実施例は有毒物質の溶出防止効果に優れてい
ることが証明された。
It can be seen from Table 1 that the examples of the present invention have a total pore volume of 1/10 or less that of the comparative examples and are dense, so that the bending strength is improved 6 to 7 times. Also,
In Examples 2 and 3 in which the mold was mirror-finished and molded, solidified products having a clean gloss were obtained. Further, from the results of Table 2, it was proved that the examples of the present invention are excellent in the elution prevention effect of toxic substances.

【0030】[0030]

【発明の効果】本発明は以上の様に構成されており、低
水セメント比で初期水和の促進された原料ペーストを用
いることによって、高強度で緻密、かつ安全な焼却灰の
セメント固化品を得ることができた。また金型表面を滑
らかな鏡面仕様とすることによって、表面光沢に優れた
セメント固化品を得ることができるので、焼却灰の資源
活用の可能性を広げることに成功した。
EFFECTS OF THE INVENTION The present invention is configured as described above, and by using a raw material paste whose initial hydration is promoted at a low water cement ratio, a cement solidified product of incineration ash having high strength, compactness and safety. I was able to get Also, by making the mold surface a smooth mirror surface, it is possible to obtain a cement-solidified product with excellent surface gloss, and we succeeded in expanding the possibilities of resource utilization of incinerated ash.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C04B 24:24) Z 2102−4G (72)発明者 沢田 三郎 兵庫県神戸市中央区脇浜町1丁目3番18号 株式会社神戸製鋼所神戸本社内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification code Internal reference number FI technical display location C04B 24:24) Z 2102-4G (72) Inventor Saburo Sawada 1 Wakihama-cho, Chuo-ku, Kobe-shi, Hyogo Chome 3-18 Kobe Steel, Ltd. Kobe Head Office

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 ごみ・下水汚泥等の焼却灰、セメント、
骨材、水を吸収した吸水性ポリマーを含む原料を混練し
て初期水和が促進されたペースト状にした後に成形を行
なうことを特徴とする焼却灰のセメント固化方法。
[Claim 1] Incinerated ash of waste, sewage sludge, cement,
A method for solidifying cement of incinerated ash, which comprises kneading an aggregate and a raw material containing a water-absorbing polymer that has absorbed water to form a paste in which initial hydration is promoted, and then forming the paste.
【請求項2】 請求項1に記載の原料が、焼却灰100
重量部に対してセメント:65重量部以上、骨材:50
重量部以上、吸水性ポリマー(乾燥時):0.5重量部
以上、水:焼却灰とセメントの合計量の25〜45重量
%含むものである請求項1に記載の焼却灰のセメント固
化方法。
2. The raw material according to claim 1 is incinerated ash 100.
Cement: 65 parts by weight or more with respect to parts by weight, aggregate: 50
The cement solidification method for incinerated ash according to claim 1, wherein the content of water-absorbent polymer (when dried): 0.5 part by weight or more and water: 25 to 45 wt% of the total amount of incinerated ash and cement.
【請求項3】 請求項1〜2に記載の方法を用いて固化
されたことを特徴とする焼却灰のセメント固化品。
3. A cement-solidified product of incineration ash, which is solidified by using the method according to claim 1.
JP26189692A 1992-09-30 1992-09-30 Cement solidification of incineration ash and cement solidified product of incineration ash Withdrawn JPH06106153A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP26189692A JPH06106153A (en) 1992-09-30 1992-09-30 Cement solidification of incineration ash and cement solidified product of incineration ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP26189692A JPH06106153A (en) 1992-09-30 1992-09-30 Cement solidification of incineration ash and cement solidified product of incineration ash

Publications (1)

Publication Number Publication Date
JPH06106153A true JPH06106153A (en) 1994-04-19

Family

ID=17368266

Family Applications (1)

Application Number Title Priority Date Filing Date
JP26189692A Withdrawn JPH06106153A (en) 1992-09-30 1992-09-30 Cement solidification of incineration ash and cement solidified product of incineration ash

Country Status (1)

Country Link
JP (1) JPH06106153A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001354465A (en) * 2000-04-13 2001-12-25 Tokyoto Gesuido Service Kk Concrete
KR100327826B1 (en) * 1999-11-18 2002-03-09 소양섭 Treatment method of waste ash included a heavy metal
KR100941047B1 (en) * 2007-06-20 2010-02-05 강릉원주대학교산학협력단 Solidification agent, and the nonsintering clay bricks and process for preparing the bricks using the agent
JP2011116657A (en) * 2000-04-13 2011-06-16 Tokyo Metropolitan Sewerage Service Corp Concrete

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100327826B1 (en) * 1999-11-18 2002-03-09 소양섭 Treatment method of waste ash included a heavy metal
JP2001354465A (en) * 2000-04-13 2001-12-25 Tokyoto Gesuido Service Kk Concrete
JP2011116657A (en) * 2000-04-13 2011-06-16 Tokyo Metropolitan Sewerage Service Corp Concrete
KR100941047B1 (en) * 2007-06-20 2010-02-05 강릉원주대학교산학협력단 Solidification agent, and the nonsintering clay bricks and process for preparing the bricks using the agent

Similar Documents

Publication Publication Date Title
JPH06106153A (en) Cement solidification of incineration ash and cement solidified product of incineration ash
JP2006222104A (en) Electromagnetic wave absorbing composition
JP2003313553A (en) Soil-stabilizing material and molded product made of soil
JP3072423B2 (en) Manufacturing method of high-strength artificial aggregate
JP2000044305A (en) Method for reclaiming and reutilizing scrapped poly(vinyl chloride)-based resins and other refuse
JP2002011366A (en) Ash grinding method and solidified molding of ash
JPH11319894A (en) Solidifier for sludge, molded part using this and solidification process thereof
JP2003012361A (en) Instant stripping porous concrete compact
JPH1029841A (en) Production of artificial aggregate
JPH0796263A (en) Method and apparatus for treating incineration ash of waste
JP4014400B2 (en) Soil treatment material composition and method for producing the same
JP2002018411A (en) Method for solidifying and molding ash
JP3499537B2 (en) Raw consludge granular material and method for producing the same
JP3275155B2 (en) Method for producing raw consludge granular material
JPH08224557A (en) Waste granular material and its production
JPH0912348A (en) Production of cured body of fine powder
JPH11189455A (en) High strength cement composition, and block for building and aggregate for building by using the same
JP4340057B2 (en) Method for producing hydrothermal solidified body
JP3526639B2 (en) Cement composition for dewatering press molding and method for producing cement molding using the same
HU212233B (en) Method for immobilization of dangerouos solid wastes
JP4077226B2 (en) Method for producing hydrothermal solidified body
JPH08198648A (en) Production of coal ash material solidified matter
JPH06233976A (en) Solidification of incineration ash and producing device of solidified molding of incineration ash
JP3263648B2 (en) Calcium silicate molding composition containing incinerated ash molten slag
JPH0423608B2 (en)

Legal Events

Date Code Title Description
A300 Application deemed to be withdrawn because no request for examination was validly filed

Free format text: JAPANESE INTERMEDIATE CODE: A300

Effective date: 19991130