JP2003235343A - Method for producing porous granular body having raw material inorganic waste - Google Patents

Method for producing porous granular body having raw material inorganic waste

Info

Publication number
JP2003235343A
JP2003235343A JP2002044252A JP2002044252A JP2003235343A JP 2003235343 A JP2003235343 A JP 2003235343A JP 2002044252 A JP2002044252 A JP 2002044252A JP 2002044252 A JP2002044252 A JP 2002044252A JP 2003235343 A JP2003235343 A JP 2003235343A
Authority
JP
Japan
Prior art keywords
inorganic waste
weight
parts
raw material
producing
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
Application number
JP2002044252A
Other languages
Japanese (ja)
Other versions
JP3628661B2 (en
Inventor
Katsuya Morimoto
勝哉 森本
Taisuke Shibata
泰典 柴田
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.)
Kawasaki Heavy Industries Ltd
Original Assignee
Kawasaki Heavy Industries 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 Kawasaki Heavy Industries Ltd filed Critical Kawasaki Heavy Industries Ltd
Priority to JP2002044252A priority Critical patent/JP3628661B2/en
Publication of JP2003235343A publication Critical patent/JP2003235343A/en
Application granted granted Critical
Publication of JP3628661B2 publication Critical patent/JP3628661B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Landscapes

  • Curing Cements, Concrete, And Artificial Stone (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)
  • Fertilizers (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)
  • Glanulating (AREA)
  • Cultivation Of Plants (AREA)
  • Combined Means For Separation Of Solids (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for producing with a technique with small environmental loading a porous granular body having the quality of a gardening material, a construction material, a soil improvement material, or the like. <P>SOLUTION: This method for producing the porous granular body comprises using as the raw material inorganic waste such as molding sand dust, crushed stone sludge, construction sludge, water supply sludge and coal ash, adding a lime raw material and water thereto, producing a kneaded product of a funicular I and II state to a capillary state by medium speed kneading, and forming the product by vibration if necessary and subjecting the product to a hydrothermal treatment, and further to a crushing treatment and a classification treatment if necessary. <P>COPYRIGHT: (C)2003,JPO

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、有効利用が進んで
いない鋳物砂ダスト、砕石スラッジ、建設汚泥、上水汚
泥、石炭灰等のシリカ(SiO2)を多く含む粉末状あ
るいは泥状廃棄物を原料とし、石灰源材料と水の添加を
行って、中速混練で製造したファニキュラーI、II状態
〜キャピラリー状態の混練物を、必要に応じて振動成形
後、水熱処理を行い、さらに必要に応じて破砕処理、分
級処理を行うことにより、園芸材、土壌改良材、土木資
材などとして利用できる多孔質粒状体の製造方法に関す
るものである。
TECHNICAL FIELD The present invention relates to a powdery or muddy waste material containing a large amount of silica (SiO 2 ) such as foundry sand dust, crushed stone sludge, construction sludge, tap water sludge, coal ash, etc. which have not been effectively utilized. As a raw material, the lime source material and water are added, and the kneaded material in the funicular I, II state to the capillary state produced by medium-speed kneading is subjected to vibration molding, if necessary, and hydrothermal treatment is performed, and further The present invention relates to a method for producing a porous granular material that can be used as a horticultural material, a soil improving material, a civil engineering material, etc. by performing a crushing treatment and a classification treatment according to the above.

【0002】[0002]

【従来の技術】例えば、特開平6−93260号公報に
は、無機系廃棄物(廃鋳物砂)に高炉スラグ、カリウム
化合物等を添加し、造粒後、850〜1300℃で焼成
を行うことにより、肥料効果を有する土壌改良材を製造
する技術が記載されている。この技術では、焼成処理が
高温のため、エネルギーを多く使用し、環境負荷が大き
い。また、粒状体品質として、溶出液pHは中性付近であ
るが、吸水率、陽イオン交換能力は小さい。さらに、粒
状体の色は無機系廃棄物の組成等により、灰色、茶色、
黒色などまちまちである。
2. Description of the Related Art For example, in Japanese Unexamined Patent Publication (Kokai) No. 6-93260, blast furnace slag, potassium compound, etc. are added to inorganic waste (waste foundry sand), and after granulation, firing is performed at 850 to 1300 ° C. Describes a technique for producing a soil conditioner having a fertilizer effect. In this technique, since the firing process is performed at a high temperature, a large amount of energy is used and the environmental load is large. As for the quality of the granular material, the pH of the eluate is near neutral, but the water absorption rate and cation exchange capacity are small. Furthermore, the color of the granules depends on the composition of the inorganic waste, gray, brown,
There are various colors such as black.

【0003】また、特開2001−121196号公
報、特開2001−122647号公報には、無機系廃
棄物(泥土スラッジ)にカルシウム化合物を添加し、4
00〜800rpm(フルード数として2.5以上)の高
速攪拌にて造粒後、130〜300℃で水熱処理を行う
ことにより、コンクリート細骨材、路盤材、園芸資材な
どに利用できる骨材を製造する方法が記載されている。
この方法は、高速による攪拌造粒であり、少ない水量で
緻密な略球状体を製造するものである。したがって、水
熱反応の進行が不十分となり、吸水率が25%以下と小
さく、かつ骨材の強度も低く、未反応CaOの残存によ
り溶出液が高pHとなる。さらに、粒状体の色は無機系廃
棄物の組成等により、灰色、茶色、黒色などまちまちで
ある。
Further, in Japanese Patent Laid-Open Nos. 2001-121196 and 2001-122647, a calcium compound is added to inorganic waste (mud sludge), and
Aggregate that can be used for concrete fine aggregate, roadbed material, horticultural material, etc. by granulating by high speed stirring of 00-800 rpm (Flude number is 2.5 or more) and then hydrothermal treatment at 130-300 ° C. A method of manufacturing is described.
This method is agitation granulation at a high speed, and produces a dense substantially spherical body with a small amount of water. Therefore, the progress of the hydrothermal reaction becomes insufficient, the water absorption rate is as small as 25% or less, the strength of the aggregate is low, and the unreacted CaO remains, so that the eluate has a high pH. Further, the color of the granular material varies depending on the composition of the inorganic waste and the like, such as gray, brown, and black.

【0004】また、特開昭55−124599号公報に
は、無機系廃棄物(汚泥)にカルシウム成分を添加し、
成形(加圧、転動、押し出し等)後、1〜20kg/cm2
(100〜211℃)で水熱処理を行うことにより、埋
め立て用などに利用できる骨材を製造する方法が記載さ
れている。この技術では、成形が加圧、転動、高圧押し
出しなどにて、円柱物、球状物を得る方法であるので、
混練物状態はファニキュラーI状態と考えられ、しか
も、圧力をかけない振動成形とは異なる方式による成形
である。したがって、骨材特性として、粒度が大きく、
粒度幅が小さく、さらに、吸水率が小さく、かつ骨材の
強度も低く、未反応CaOの残存により溶出液が高pHと
なる。さらに、骨材の色は、無機系廃棄物の組成等によ
り、灰色、茶色、黒色などまちまちである。以上より、
従来の技術では、環境負荷の小さい技術により、用途に
応じた色の多孔質な粒状体を製造することが困難であ
る。
Further, in JP-A-55-124599, a calcium component is added to inorganic waste (sludge),
After molding (pressurization, rolling, extrusion, etc.), 1 to 20 kg / cm 2
It describes a method for producing an aggregate that can be used for landfilling, etc. by performing hydrothermal treatment at (100 to 211 ° C.). In this technology, molding is a method of obtaining a cylindrical object and a spherical object by pressing, rolling, high-pressure extrusion, etc.
The state of the kneaded material is considered to be the funicular I state, and the molding is performed by a method different from the vibration molding in which no pressure is applied. Therefore, as an aggregate characteristic, the particle size is large,
The particle size width is small, the water absorption rate is small, the strength of the aggregate is low, and the pH of the eluate becomes high due to the residual unreacted CaO. Furthermore, the color of the aggregate varies depending on the composition of the inorganic waste and the like, such as gray, brown, and black. From the above,
With the conventional technology, it is difficult to manufacture a porous granular material having a color according to the application by a technology having a low environmental load.

【0005】[0005]

【発明が解決しようとする課題】上述したように、無機
系廃棄物を原料として安全で利用価値の高い多孔質粒状
体を製造する技術では、処理温度があまり高温となら
ず、少ないエネルギー量で粒状体を製造できる環境負荷
の小さい技術の開発が望まれている。また、上述の従来
技術で製造された粒状体では、園芸材として用いる場合
に必要な特性である、吸水率、陽イオン交換容量、溶出
液pHに問題があり、園芸材としての品質を満足する粒状
体、すなわち、高い吸水率、高い陽イオン交換容量を有
し、溶出液pHが低い粒状体を製造できる技術の開発が望
まれている。
As described above, in the technology for producing a safe and highly useful porous granular material using inorganic waste as a raw material, the treatment temperature does not become too high, and the amount of energy is small. It is desired to develop a technology with a low environmental load capable of producing granular materials. Further, in the above-mentioned granular material manufactured by the conventional technique, there are problems in water absorption rate, cation exchange capacity, and eluate pH, which are properties required when used as a gardening material, and satisfy the quality as a gardening material. It is desired to develop a technique capable of producing a granular body, that is, a granular body having a high water absorption rate, a high cation exchange capacity, and a low eluent pH.

【0006】また、上述の従来技術で製造された粒状体
では、土木材として用いる場合に必要な特性である、粒
度分布、締め固め特性、強度に問題があり、土木材とし
ての品質を満足する粒状体、すなわち、幅広い粒度分
布、優れた締め固め特性、高強度を有する粒状体を製造
できる技術の開発が望まれている。また、上述したよう
に、従来技術では粒状体の色が廃棄物組成等によりまち
まちであったが、廃棄物の組成や色に左右されずに、用
途に応じた色を有する多孔質粒状体を製造する技術の開
発が望まれている。さらに、安全性において、溶出液が
土壌環境基準を満足することが必要である。
Further, the above-mentioned granular material produced by the conventional technique has problems in particle size distribution, compaction characteristics and strength, which are characteristics required when used as soil wood, and satisfies the quality as soil wood. It is desired to develop a technique capable of producing granules, that is, granules having a wide particle size distribution, excellent compaction characteristics, and high strength. Further, as described above, in the prior art, the color of the granular material was varied depending on the waste composition and the like, but a porous granular material having a color according to the application is not affected by the composition and color of the waste material. Development of manufacturing technology is desired. Furthermore, in terms of safety, it is necessary that the eluate satisfy the soil environmental standards.

【0007】本発明は上記の諸点に鑑みなされたもの
で、本発明の目的は、鋳物砂ダスト、砕石スラッジ、建
設汚泥、上水汚泥、石炭灰等の無機系廃棄物に対し、石
灰源材料と水の添加を行い、フルード数0.1〜2.
0、好ましくは0.5〜1.5の中速混練で製造したフ
ァニキュラーI、II状態〜キャピラリー状態の混練物
を、必要に応じて振動成形後、水熱処理を行い、さらに
必要に応じて破砕処理、分級処理を行うことにより、園
芸材、土壌改良材、土木資材などとして利用できる吸水
率30%以上の多孔質粒状体を製造する方法を提供する
ことにある。
The present invention has been made in view of the above points, and an object of the present invention is to provide a lime source material for inorganic waste such as foundry sand dust, crushed stone sludge, construction sludge, tap water sludge and coal ash. And water were added, and the Froude number was 0.1-2.
A kneaded product of 0, preferably 0.5 to 1.5, in a medium speed kneading, in a funicular I, II state to a capillary state is subjected to vibration molding, if necessary, and then subjected to hydrothermal treatment, and further, if necessary. An object of the present invention is to provide a method for producing a porous granular material having a water absorption rate of 30% or more, which can be used as a horticultural material, a soil improving material, a civil engineering material, etc. by performing a crushing treatment and a classification treatment.

【0008】[0008]

【課題を解決するための手段】上記の目的を達成するた
めに、本発明の無機系廃棄物を原料とする多孔質粒状体
の製造方法は、無機系廃棄物100重量部に、石灰源材
料2.5〜25重量部及び必要に応じて水0.01〜3
0重量部を加えて混練機に投入し、フルード数が0.1
〜2.0、好ましくは0.5〜1.5となるように中速
で混練を行って含水率20%以上のファニキュラーI状
態の略球状に造粒された混練物とし、該混練物を3〜1
0mmで分級して、3〜10mm以上のものは破砕処理した
後、前記混練機又は投入原料に戻し、3〜10mm以下の
ものを常温〜95℃で0.2〜36時間養生を行った
後、130〜220℃で1〜24時間水熱処理を行うよ
うに構成されている(図1参照)。上記の方法において
は、水熱処理で得られた粒状体を0.1〜1mmで分級
し、0.1〜1mm以下のものを混練機又は投入原料に戻
してもよい(図2参照)。
In order to achieve the above object, a method for producing a porous granular material using an inorganic waste as a raw material according to the present invention comprises 100 parts by weight of the inorganic waste and a lime source material. 2.5 to 25 parts by weight and, if necessary, water 0.01 to 3
Add 0 parts by weight and add to a kneader to obtain a Froude number of 0.1.
To 2.0, preferably 0.5 to 1.5, and kneading at a medium speed to obtain a substantially spherical granulated kneaded product in a funicular I state having a water content of 20% or more. 3 to 1
After classifying at 0 mm, crushing 3 to 10 mm or more after crushing, returning to the kneading machine or input material, and curing at 3 to 10 mm or less at room temperature to 95 ° C for 0.2 to 36 hours , 130 to 220 ° C. for 1 to 24 hours (see FIG. 1). In the above method, the granules obtained by the hydrothermal treatment may be classified to 0.1 to 1 mm, and those having a size of 0.1 to 1 mm or less may be returned to the kneader or the charging raw material (see FIG. 2).

【0009】また、本発明の方法は、無機系廃棄物10
0重量部に、石灰源材料2.5〜25重量部及び必要に
応じて水0.01〜60重量部を加えて混練機に投入
し、フルード数が0.1〜2.0、好ましくは0.5〜
1.5となるように中速で混練を行って含水率30%以
上のファニキュラーII状態乃至キャピラリー状態の混練
物とし、該混練物を常温〜95℃で0.2〜36時間養
生を行い、ついで、130〜220℃で1〜24時間水
熱処理を行った後、破砕処理を行うことを特徴としてい
る(図3参照)。
The method of the present invention is also applied to the inorganic waste 10
To 25 parts by weight, 2.5 to 25 parts by weight of the lime source material and, if necessary, 0.01 to 60 parts by weight of water are added and charged into a kneader, and the Froude number is 0.1 to 2.0, preferably 0.5 ~
The mixture is kneaded at a medium speed to give a kneaded product having a water content of 30% or more in a funicular II state or a capillary state, and the kneaded product is aged at room temperature to 95 ° C for 0.2 to 36 hours. Then, a hydrothermal treatment is performed at 130 to 220 ° C. for 1 to 24 hours, and then a crushing treatment is performed (see FIG. 3).

【0010】また、本発明の方法は、原料である無機系
廃棄物100重量部に、石灰源材料2.5〜25重量部
及び必要に応じて水0.01〜60重量部を加えて混練
機に投入し、フルード数が0.1〜2.0、好ましくは
0.5〜1.5となるように中速で混練を行って含水率
30%以上のファニキュラーII状態乃至キャピラリー状
態の混練物とし、該混練物を振動成形した後、常温〜9
5℃で0.2〜36時間養生を行い、ついで、130〜
220℃で1〜24時間水熱処理を行った後、破砕処理
を行うことを特徴としている(図4参照)。
In the method of the present invention, 2.5 to 25 parts by weight of the lime source material and 0.01 to 60 parts by weight of water are added to 100 parts by weight of the inorganic waste as a raw material and kneaded. It is charged into a machine and kneaded at a medium speed so that the Froude number is from 0.1 to 2.0, preferably from 0.5 to 1.5. After kneading and vibration-molding the kneading product, the mixture is kept at room temperature to 9
Curing at 5 ℃ for 0.2 ~ 36 hours, then 130 ~
The hydrothermal treatment is performed at 220 ° C. for 1 to 24 hours, and then the crushing treatment is performed (see FIG. 4).

【0011】これらの場合、前処理として、無機系廃棄
物100重量部に、硝酸塩などの酸化剤0.5〜20重
量部及び必要に応じて水0.01〜60重量部を加えて
混練し、得られた混練物を常温〜220℃で0.2〜1
5時間加熱処理又は水熱処理した後、得られた処理物に
石灰源材料及び必要に応じて水を加えて上記のいずれか
の処理を行うことができる(図5参照)。また、無機系
廃棄物100重量部に、石灰源材料2.5〜25重量
部、硝酸塩などの酸化剤0.5〜20重量部、及び必要
に応じて水0.01〜60重量部を加えて混練機に投入
し、フルード数が0.1〜2.0、好ましくは0.5〜
1.5となるように中速で混練を行って含水率30%以
上のファニキュラーII状態乃至キャピラリー状態の混練
物とし、該混練物に対して上記の養生、水熱処理、破砕
処理、又は振動成形、養生、水熱処理、破砕処理を行う
こともできる(図6参照)。
In these cases, as pretreatment, 0.5 to 20 parts by weight of an oxidizing agent such as nitrate and 0.01 to 60 parts by weight of water are added to 100 parts by weight of inorganic waste and kneaded. The obtained kneaded product is 0.2 to 1 at room temperature to 220 ° C.
After the heat treatment or the hydrothermal treatment for 5 hours, one of the above treatments can be performed by adding a lime source material and water if necessary to the obtained treated product (see FIG. 5). To 100 parts by weight of inorganic waste, 2.5 to 25 parts by weight of lime source material, 0.5 to 20 parts by weight of an oxidizing agent such as nitrate, and 0.01 to 60 parts by weight of water are added if necessary. And put into a kneader, and the Froude number is 0.1 to 2.0, preferably 0.5 to
The mixture is kneaded at a medium speed to give a kneaded product having a water content of 30% or more in a funicular II state or a capillary state, and the kneaded product is subjected to the above-mentioned curing, hydrothermal treatment, crushing treatment, or vibration. Molding, curing, hydrothermal treatment, and crushing treatment can also be performed (see FIG. 6).

【0012】また、これらの方法においては、まず無機
系廃棄物を破砕した後に、上記のいずれかの処理を行っ
てもよい(図7参照)。また、これらの方法において
は、まず無機系廃棄物を0.05〜0.3mmで分級を行
って粗粒子の除去を行い、微粒子は上記のいずれかの処
理を行い、粗粒子は水熱処理後の処理物と混合するよう
にしてもよい(図8参照)。また、これらの方法におい
ては、水熱処理し破砕した後の粒状体を0.05〜0.
3mmで分級して微粒子の除去を行い、微粒子を投入原料
又は混練機に戻すようにしてもよい(図9参照)。
Further, in these methods, any of the above treatments may be carried out after first crushing the inorganic waste (see FIG. 7). In addition, in these methods, first, the inorganic waste is classified by 0.05 to 0.3 mm to remove coarse particles, the fine particles are subjected to any of the above treatments, and the coarse particles are subjected to a hydrothermal treatment. You may make it mix with the processed material (refer FIG. 8). In addition, in these methods, the granular material after hydrothermal treatment and crushing is added in an amount of 0.05 to 0.
The particles may be classified by 3 mm to remove the particles, and then the particles may be returned to the charging material or the kneader (see FIG. 9).

【0013】本発明は、以上のような多孔質粒状体の製
造方法であり、具体的には、次のような手段を講じるこ
とにより、環境負荷の小さい技術で、優れた特性を有す
る粒状体を製造することができる。 (1)環境負荷の小さい技術 処理温度が高いほどエネルギーが多く必要であり、環境
負荷を低減させるには、処理温度の低下が有効である。
そこで、130〜220℃の温度で水熱処理を行う。1
30℃未満では反応速度が遅く、未反応の石灰が残存
し、低強度であるとともに、粒状体溶出液pHが高くな
る。220℃を超えると圧力が高くなり、装置コストが
高くなる。
The present invention is a method for producing a porous granular material as described above, and specifically, by taking the following means, a granular material having excellent characteristics with a technology having a small environmental load. Can be manufactured. (1) Technology with low environmental load The higher the processing temperature, the more energy is required, and in order to reduce the environmental load, lowering the processing temperature is effective.
Therefore, hydrothermal treatment is performed at a temperature of 130 to 220 ° C. 1
If the temperature is lower than 30 ° C, the reaction rate is slow, unreacted lime remains, the strength is low, and the pH of the granular material eluate is high. If it exceeds 220 ° C, the pressure becomes high and the cost of the apparatus becomes high.

【0014】(2)高強度 無機系廃棄物のSiO2含有量、水分量等により、石灰
源材料の添加量を2.5〜25重量部の範囲で調整し、
ファニキュラーI、II状態〜キャピラリー状態となるよ
うに水を徐々に加え、中速混練を行うことにより、石灰
源材料、水が均一に分散され、水熱処理にて、高強度を
有する多孔質粒状体が得られる。石灰源材料の添加量が
2.5重量部よりも少ないと高強度を発現せず、25重
量部よりも多いとコスト高になるとともに、未反応石灰
が多く残存し、粒状体の品質が悪くなる。また、混練物
を常温〜95℃で0.2〜36時間養生を行うことによ
り、水和反応が進行し、表面水がなくなるので、その後
の水熱処理で粒子同士がくっつかず、かつ高強度を発現
する。95℃を超える温度、36時間より長時間での処
理はコスト高となり、0.2時間未満の処理では養生が
不十分で、強度が低下する。
(2) The addition amount of the lime source material is adjusted in the range of 2.5 to 25 parts by weight according to the SiO 2 content and the water content of the high-strength inorganic waste.
By gradually adding water so as to be in the funicular I and II state to the capillary state, and kneading at a medium speed, the lime source material and water are uniformly dispersed, and porous granules having high strength by hydrothermal treatment. The body is obtained. If the amount of the lime source material added is less than 2.5 parts by weight, high strength will not be exhibited, and if it is more than 25 parts by weight, the cost will increase and a large amount of unreacted lime will remain, resulting in poor quality of granules. Become. Further, by aging the kneaded product at room temperature to 95 ° C. for 0.2 to 36 hours, the hydration reaction proceeds and the surface water disappears, so particles do not stick to each other in the subsequent hydrothermal treatment, and high strength is obtained. Express. The treatment at a temperature higher than 95 ° C. for a time longer than 36 hours becomes high in cost, and the treatment for less than 0.2 hours causes insufficient curing and lowers the strength.

【0015】(3)園芸材としての特性 a)高い吸水率 無機系廃棄物における塑性限界は20〜70%と幅広
い。塑性限界が約30%以上の無機系廃棄物において
は、中速混練を行うことにより、吸水率30%以上の粒
状体を容易に製造できる。塑性限界が約30%未満の無
機系廃棄物は、0.05〜0.3mmで分級を行い、粗粒
子を除去するか、あるいは破砕処理を行い、0.1mm以
上の粒子を少なくすることにより、あるいは微粒子の多
孔質粒状体を原料に添加することにより、無機系廃棄物
の塑性限界を30%程度とすることができる。水熱処理
を速やかに、均一に進行させ、多孔質な粒状体とするた
めには、中速混練にて、混練物をファニキュラーI、II
状態〜キャピラリー状態とすることが重要である。ここ
で中速混練とは、フルード数が0.1〜2.0、好まし
くは0.5〜1.5となる条件で混練することである。
なお、フルード数は、N2R/g(N:回転数、R:攪
拌翼径、g:重力加速度)で表される無次元数であり、
本発明では混練速度に対応している。低速混練では混練
物の均一化に長時間を要し、高速混練では水量が少なく
なり、緻密化するので、多孔質粒状体とならず、さら
に、短時間に混練物状態が変化し、所定の混練物とする
ために混練機操作条件の制御が難しくなる。混練物がフ
ァニキュラーI状態にならないペンデュラー状態では、
水和反応が十分進行せず、低強度で、陽イオン交換容量
が小さくなる。また、キャピラリー状態以上の混練物状
態、すなわちスラリーでは混練物が流動し、ハンドリン
グが難しくなり、装置の安定運転が難しくなる。なお、
ファニキュラーII状態、キャピラリー状態とは、JIS
A 1205(土の液性限界・塑性限界試験方法)に
よって測定された塑性限界、液性限界の状態を指す。
(3) Characteristics as a gardening material a) High water absorption The plastic limit of inorganic wastes is as wide as 20 to 70%. For inorganic wastes having a plasticity limit of about 30% or more, medium speed kneading can easily produce granules having a water absorption rate of 30% or more. Inorganic waste with a plasticity limit of less than about 30% is classified by 0.05 to 0.3 mm to remove coarse particles or crushed to reduce particles of 0.1 mm or more. Alternatively, the plastic limit of the inorganic waste can be set to about 30% by adding fine particles of porous granular material to the raw material. In order to rapidly and uniformly proceed the hydrothermal treatment to form a porous granular material, the kneaded product is treated with Funicular I and II by medium speed kneading.
It is important to set the state to the capillary state. Here, the medium speed kneading is kneading under the condition that the Froude number is 0.1 to 2.0, preferably 0.5 to 1.5.
The Froude number is a dimensionless number represented by N 2 R / g (N: rotational speed, R: stirring blade diameter, g: gravitational acceleration),
The present invention corresponds to the kneading speed. In low-speed kneading, it takes a long time to homogenize the kneaded product, and in high-speed kneading, the amount of water decreases and the mixture is densified. Since it is a kneaded product, it becomes difficult to control the operating conditions of the kneader. In the pendular state where the kneaded product does not enter the funicular I state,
The hydration reaction does not proceed sufficiently, the strength is low, and the cation exchange capacity is small. Further, in a kneaded product state that is higher than the capillary state, that is, in a slurry, the kneaded product flows, and handling becomes difficult, and stable operation of the device becomes difficult. In addition,
According to JIS, the funicular II state and the capillary state are
A 1205 refers to the state of plasticity limit and liquidity limit measured by the soil liquidity limit / plasticity limit test method.

【0016】b)適正な粒度(高い透水性の確保) 粒状体に3〜10mm以上の粗粒子ができないようにする
には、混練物を3〜10mmで分級し、粗粒子は破砕して
から混練工程(又は原料工程)に戻し、3〜10mm以下
の粒子を水熱処理すればよい。一方、0.1〜1mm以下
の微粒子は、水熱処理後に分級して除去すればよい。さ
らに、水熱処理後に破砕して生じた0.05〜0.3mm
以下の微粒子は、破砕処理後に分級して除去すればよ
い。微粒子は混練工程(又は原料工程)に戻すことによ
り、全量の廃棄物を粒状体とすることができる。
B) Appropriate particle size (securing high water permeability) In order to prevent coarse particles of 3 to 10 mm or more from forming in the granular material, the kneaded product is classified by 3 to 10 mm and the coarse particles are crushed. Returning to the kneading step (or raw material step), the particles of 3 to 10 mm or less may be hydrothermally treated. On the other hand, fine particles of 0.1 to 1 mm or less may be removed by classification after hydrothermal treatment. Furthermore, 0.05-0.3mm generated by crushing after hydrothermal treatment
The following fine particles may be classified and removed after the crushing treatment. By returning the fine particles to the kneading step (or the raw material step), the entire amount of waste can be made into particles.

【0017】c)高い陽イオン交換容量 水熱処理による生成物はトバモライト系物質である。ト
バモライト系物質は陽イオン交換能力を有しているの
で、この量を多くすることが重要である。無機系廃棄物
に石灰系材料を2.5〜25重量%添加することによ
り、トバモライト系物質の生成が可能で、高い陽イオン
交換容量を確保できる。石灰系材料の量が多くなると、
コスト高になるとともに、未反応の石灰系材料が残存
し、溶出液pHが高くなる。石灰系材料としては、生石
灰、消石灰、セメント、粉末スラグ、廃コンクリート微
粉などが適している。特に、生石灰がコスト、粒状体性
能、装置の安定運転性等より優れている。 d)長期的な透水性の確保 高い強度が長期的に保持されるので、大きい透水性が長
期的に確保される。
C) High cation exchange capacity The product of hydrothermal treatment is a tobermorite material. Since the tobermorite-based substance has a cation exchange ability, it is important to increase this amount. By adding 2.5 to 25% by weight of a lime-based material to the inorganic waste, it is possible to generate a tobermorite-based substance and secure a high cation exchange capacity. When the amount of lime-based material increases,
As the cost increases, unreacted lime-based material remains and the pH of the eluate increases. As the lime-based material, quick lime, slaked lime, cement, powder slag, waste concrete fine powder and the like are suitable. In particular, quick lime is superior in cost, granular performance, and stable operability of the device. d) Ensuring long-term water permeability Since high strength is maintained for a long time, large water permeability is ensured for a long time.

【0018】(4)土木材としての特性(締め固め特
性、修正CBR特性) 破砕処理条件にて、クラッシャランC−40(最大径4
0mm)、C−20(最大径20mm)、F−2.5(最大
径5mm)などの粒度とすることができる。分級機と併用
すれば、粒度調整砕石の粒度とすることができる。ま
た、粒子形状は略球状体よりも不定形の方が、粒子同士
の絡み合いが強く、締め固め特性が良好で、修正CBR
が高くなる。したがって、最大径、粒度分布、粒形によ
るが、破砕処理による不定形粒子は、天然材相当の締め
固めで、修正CBR30〜130%とすることができ、
各種の土木材としての適用が可能である。また、高い吸
水率と大きい透水係数を有しているので、排水性が要求
される運動場などへの適用も可能である。
(4) Characteristics as soil wood (compacting characteristics, modified CBR characteristics) Crusher Run C-40 (maximum diameter 4
0 mm), C-20 (maximum diameter 20 mm), F-2.5 (maximum diameter 5 mm) and the like. When used in combination with a classifier, the particle size of crushed stone can be adjusted. In addition, when the particle shape is irregular rather than substantially spherical, the particles are more entangled with each other, the compaction characteristics are better, and the modified CBR
Becomes higher. Therefore, depending on the maximum diameter, the particle size distribution, and the particle shape, the irregularly shaped particles obtained by the crushing treatment can be compacted to a modified CBR of 30 to 130% with compaction equivalent to that of the natural material.
It can be applied as various types of earth and wood. Further, since it has a high water absorption rate and a large water permeability, it can be applied to a playground where drainage is required.

【0019】(5)粒状体の色 粒状体の色は無機系廃棄物の色(組成等によって異な
る)によって異なり、黒色〜茶色〜灰色の色を呈する。
用途によっては、色が重要な評価項目となる。粒状体の
色の調整は、無機系廃棄物に含まれている鉄化合物を活
用する。すなわち、鉄化合物の粒度が大きければ、粉砕
することにより色が濃くなる。また、硝酸鉄、硝酸マグ
ネシウム、硝酸アルミニウムなどの酸化剤を選定し、常
温〜220℃の加熱処理あるいは水熱処理にて鉄化合物
を酸化させることにより、黒色〜茶色とすることができ
る。添加する酸化剤の種類、量、熱処理温度により色は
異なるので、目的とする色でそれらを調整する。なお、
添加する酸化剤量が少なすぎると色の変化がなく、多す
ぎるとコスト高になるとともに、粒状体品質が低下す
る。
(5) Color of Granules The color of the granules varies depending on the color of the inorganic waste (varies depending on the composition etc.), and exhibits a color of black to brown to gray.
Depending on the application, color is an important evaluation item. The iron compound contained in the inorganic waste is used to adjust the color of the granular material. That is, if the iron compound has a large particle size, the color becomes darker by crushing. Further, black to brown can be obtained by selecting an oxidizing agent such as iron nitrate, magnesium nitrate or aluminum nitrate and oxidizing the iron compound by heat treatment or hydrothermal treatment at room temperature to 220 ° C. Since the color varies depending on the type and amount of the oxidizing agent added and the heat treatment temperature, adjust them with the target color. In addition,
If the amount of the oxidizing agent added is too small, the color does not change, and if it is too large, the cost increases and the quality of the granular material deteriorates.

【0020】(6)安全性 水熱反応によるトバモライト系物質は有害物を固定する
ので、適正な処理条件による多孔質粒状体の溶出液(環
境庁告示46号法に準拠)は、土壌環境基準を満足す
る。その他、多孔質粒状体は排ガス吸着剤、水処理材、
建材添加材などへの用途にも利用ができる。
(6) Safety Since the tobermorite-based substance due to hydrothermal reaction fixes harmful substances, the eluate of the porous granular material (according to the Environmental Agency Notification No. 46 method) under proper processing conditions is a soil environmental standard. To be satisfied. In addition, porous granular materials include exhaust gas adsorbents, water treatment materials,
It can also be used as a building material additive.

【0021】[0021]

【発明の実施の形態】以下、本発明の実施の形態につい
て説明するが、本発明は下記の実施の形態に何ら限定さ
れるものではなく、適宜変更して実施することが可能な
ものである。図1は、本発明の実施の第1形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
を示している。鋳物砂ダスト、砕石スラッジ、建設汚
泥、上水汚泥、石炭灰等の無機系廃棄物に対し、生石
灰、消石灰、セメント、粉末スラグ、廃コンクリート微
粉等の石灰系材料と必要に応じて水の添加を行い、フル
ード数が0.1〜2.0、好ましくは0.5〜1.5と
なるように中速で混練を行って含水率20%以上のファ
ニキュラーI状態の略球状の造粒物(混練物)とする。
該混練物を3〜10mmでふるい等により分級し、3〜1
0mm以上のものは破砕処理した後、混練工程(又は原料
工程)に戻し、3〜10mm以下のものを常温〜95℃で
0.2〜36時間養生を行った後、130〜220℃で
1〜24時間水熱処理を行い、多孔質粒状体を得る。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, embodiments of the present invention will be described. However, the present invention is not limited to the following embodiments, and can be appropriately modified and implemented. . FIG. 1 shows steps of a method for producing a porous granular material using inorganic waste as a raw material according to the first embodiment of the present invention. Addition of lime-based materials such as quick lime, slaked lime, cement, powder slag, and waste concrete fine powder to inorganic waste such as foundry sand dust, crushed stone sludge, construction sludge, tap water sludge, and coal ash, and water if necessary. And a kneading at a medium speed so that the Froude number is 0.1 to 2.0, preferably 0.5 to 1.5, and a substantially spherical granulation in a funicular I state having a water content of 20% or more. The product (kneaded product).
The kneaded product is classified by a sieve or the like with a size of 3 to 10 mm, and then 3-1.
After crushing 0 mm or more, it is returned to the kneading step (or raw material step), and 3 to 10 mm or less is cured at room temperature to 95 ° C for 0.2 to 36 hours, and then at 130 to 220 ° C for 1 hour. Hydrothermal treatment is performed for -24 hours to obtain a porous granular material.

【0022】図2は、本発明の実施の第2形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
を示している。無機系廃棄物に対し、石灰系材料と必要
に応じて水の添加を行い、中速混練を行って含水率20
%以上のファニキュラーI状態の略球状の造粒物(混練
物)とする。該混練物を3〜10mmで分級し、3〜10
mm以上のものは破砕処理した後、混練工程(又は原料工
程)に戻し、3〜10mm以下のものは養生した後、水熱
処理を行う。水熱処理で得られた粒状体を0.1〜1mm
で分級し、0.1〜1mm以下のものを混練工程(又は原
料工程)に戻し、微粉を除去した多孔質粒状体を得る。
他の構成及び作用等は、実施の第1形態の場合と同様で
ある。
FIG. 2 shows steps of a method for producing a porous granular material using inorganic waste as a raw material according to the second embodiment of the present invention. A water content of 20 is added to the inorganic waste by adding lime-based material and water if necessary, and kneading at medium speed.
% Or more to obtain a substantially spherical granulated product (kneaded product) in the funicular I state. The kneaded product is classified into 3 to 10 mm, and 3 to 10
After crushing those having a diameter of 3 mm or more, they are returned to the kneading step (or raw material step), and those having a diameter of 3 to 10 mm or less are cured and then subjected to hydrothermal treatment. Granules obtained by hydrothermal treatment 0.1 to 1 mm
Then, the particles having a diameter of 0.1 to 1 mm or less are returned to the kneading step (or the raw material step) to obtain a porous granular material from which fine powder is removed.
Other configurations, operations and the like are similar to those of the first embodiment.

【0023】図3は、本発明の実施の第3形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
を示している。無機系廃棄物に対し、石灰系材料と必要
に応じて水の添加を行い、中速混練を行って含水率30
%以上のファニキュラーII状態〜キャピラリー状態の混
練物(塊状)とし、該混練物を常温〜95℃で0.2〜
36時間養生を行い、ついで、130〜220℃で1〜
24時間水熱処理を行った後、破砕処理を行って不定形
の多孔質粒状体を得る。他の構成及び作用等は、実施の
第1形態の場合と同様である。
FIG. 3 shows steps of a method for producing a porous granular material using inorganic waste as a raw material according to the third embodiment of the present invention. Water content of 30% is added to inorganic waste by adding lime material and water as needed and kneading at medium speed.
% Or more of a funicular II state-capillary state kneaded product (lump), and the kneaded product at room temperature to 95 ° C. of 0.2 to
Curing for 36 hours, then 1 ~ 130 ~ 220 ℃
After hydrothermal treatment for 24 hours, crushing treatment is performed to obtain amorphous porous particles. Other configurations, operations and the like are similar to those of the first embodiment.

【0024】図4は、本発明の実施の第4形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
を示している。無機系廃棄物に対し、石灰系材料と必要
に応じて水の添加を行い、中速混練を行って含水率30
%以上のファニキュラーII状態〜キャピラリー状態の混
練物(塊状)とし、該混練物を振動により圧力をかけず
に成形した後、養生を行い、ついで、水熱処理を行った
後、破砕処理を行って不定形の多孔質粒状体を得る。な
お、振動成形は、混練物を型枠に投入し、下から振動を
与えて成形するものである。他の構成及び作用等は、実
施の第1、第3形態の場合と同様である。
FIG. 4 shows steps of a method for producing a porous granular material using inorganic waste as a raw material according to the fourth embodiment of the present invention. Water content of 30% is added to inorganic waste by adding lime material and water as needed and kneading at medium speed.
% Or more of a funicular II state to a capillary state kneaded material (lump), the kneaded material is molded without applying pressure by vibration, then cured, and then subjected to hydrothermal treatment and crushing treatment. To obtain an amorphous porous granular material. In the vibration molding, the kneaded product is put into a mold, and vibration is applied from below to perform molding. Other configurations, operations and the like are similar to those of the first and third embodiments.

【0025】図5は、本発明の実施の第5形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
の一例を示している。無機系廃棄物に対し、硝酸鉄、硝
酸マグネシウム、硝酸アルミニウム等の酸化剤と必要に
応じて水の添加を行い、混練を行って混練物とし、該混
練物を常温〜220℃で0.2〜15時間加熱処理又は
水熱処理する。このような酸化処理を行った処理物に、
石灰系材料と必要に応じて水を加えて、実施の第1〜第
4形態のような処理を行う。なお、図5では、酸化処理
の後に、一例として、混練、養生、水熱処理、破砕の各
工程を図示しているが、酸化処理の後に図1〜図4に示
すような処理を行うことができる。
FIG. 5 shows an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the fifth embodiment of the present invention. To the inorganic waste, an oxidizing agent such as iron nitrate, magnesium nitrate, and aluminum nitrate and, if necessary, water are added, and kneading is performed to obtain a kneaded product. Heat treatment or hydrothermal treatment for ˜15 hours. To the processed product that has been subjected to such an oxidation treatment,
The lime-based material and water as necessary are added, and the treatments according to the first to fourth embodiments are performed. Although FIG. 5 illustrates, as an example, the steps of kneading, curing, hydrothermal treatment, and crushing after the oxidation treatment, it is possible to perform the treatments shown in FIGS. 1 to 4 after the oxidation treatment. it can.

【0026】図6は、本発明の実施の第6形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
の一例を示している。無機系廃棄物に対し、石灰系材料
及び酸化剤と必要に応じて水の添加を行い、中速混練を
行って含水率30%以上のファニキュラーII状態〜キャ
ピラリー状態の混練物(塊状)とする。該混練物を養生
し、ついで、水熱処理を行った後、破砕処理を行って不
定形の多孔質粒状体を得る。本実施の形態は、酸化処理
を別に前処理として行うのではなく、酸化剤を石灰系材
料等と一緒に添加して混練工程、養生工程等で酸化処理
も行うものである。なお、図6では、一例として、実施
の第3形態(図3)の工程において石灰系材料とともに
酸化剤を添加した構成を示しているが、実施の第4形態
(図4)の工程において石灰系材料とともに酸化剤を添
加した構成としてもよく、その場合は、混練物を振動成
形した後、養生、水熱処理、破砕を行う。他の構成及び
作用等は、実施の第1、第3、第4、第5形態の場合と
同様である。
FIG. 6 shows an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the sixth embodiment of the present invention. A lime material and an oxidizer and, if necessary, water are added to the inorganic waste, and the mixture is mixed at a medium speed to obtain a kneaded product (lump) in a funicular II state to a capillary state with a water content of 30% or more. To do. The kneaded product is cured, then hydrothermally treated, and then crushed to obtain an amorphous porous granular material. In the present embodiment, the oxidation treatment is not separately performed as a pretreatment, but the oxidation treatment is also performed in a kneading step, a curing step, etc. by adding an oxidizing agent together with a lime material or the like. Note that FIG. 6 shows, as an example, a configuration in which an oxidizing agent is added together with the lime-based material in the process of the third embodiment (FIG. 3), but lime is used in the process of the fourth embodiment (FIG. 4). The composition may be such that an oxidizing agent is added together with the system material. In that case, the kneaded product is subjected to vibration molding, followed by curing, hydrothermal treatment and crushing. Other configurations, operations and the like are similar to those of the first, third, fourth and fifth embodiments.

【0027】図7は、本発明の実施の第7形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
の一例を示している。本実施の形態は、無機系廃棄物を
破砕処理して粗粒子をなくした後で、実施の第1〜第6
形態のような処理を行うものである。なお、図7では、
破砕処理の後に、一例として、混練、養生、水熱処理、
破砕の各工程を図示しているが、破砕処理の後に図1〜
図6に示すような処理を行うことができる。
FIG. 7 shows an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the seventh embodiment of the present invention. In the present embodiment, after the inorganic waste is crushed to eliminate coarse particles, the first to sixth embodiments are performed.
The processing is performed in a form. In addition, in FIG.
After the crushing process, as an example, kneading, curing, hydrothermal treatment,
Each process of crushing is illustrated, but after the crushing process,
The processing as shown in FIG. 6 can be performed.

【0028】図8は、本発明の実施の第8形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
の一例を示している。本実施の形態は、無機系廃棄物を
0.05〜0.3mmで分級して粗粒子を除去してから、
微粒子に対して実施の第1〜第6形態のような処理を行
うものである。粗粒子は水熱処理後の処理物と混合す
る。なお、図8では、分級して粗粒子を除去した後に、
一例として、混練、養生、水熱処理、破砕の各工程を図
示しているが、分級の後に図1〜図6に示すような処理
を行うことができる。
FIG. 8 shows an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the eighth embodiment of the present invention. In the present embodiment, after the inorganic waste is classified by 0.05 to 0.3 mm to remove coarse particles,
The processing as in the first to sixth embodiments is performed on the fine particles. The coarse particles are mixed with the processed product after the hydrothermal treatment. In FIG. 8, after removing coarse particles by classification,
As an example, the steps of kneading, curing, hydrothermal treatment, and crushing are illustrated, but the treatments shown in FIGS. 1 to 6 can be performed after classification.

【0029】図9は、本発明の実施の第9形態による無
機系廃棄物を原料とする多孔質粒状体の製造方法の工程
の一例を示している。本実施の形態は、水熱処理し破砕
した後の破砕物(粒状体)を0.05〜0.3mmで分級
して微粒子の除去を行い、微粒子を原料工程(又は混練
工程)に戻し、微粒子を除去した多孔質粒状体を得るも
のである。なお、図9では、一例として、混練、養生、
水熱処理、破砕の工程の後に分級を行う構成としている
が、分級の前に図3〜図8に示すような処理を行うこと
ができる。
FIG. 9 shows an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the ninth embodiment of the present invention. In the present embodiment, the crushed material (granular material) after hydrothermal treatment and crushing is classified to 0.05 to 0.3 mm to remove fine particles, and the fine particles are returned to the raw material step (or kneading step). To obtain a porous granular material. In FIG. 9, as an example, kneading, curing,
Although the classification is performed after the hydrothermal treatment and crushing steps, the treatments shown in FIGS. 3 to 8 can be performed before the classification.

【0030】[0030]

【実施例】実施例1 鋳物砂ダストA(SiO2:65wt%、塑性限界:32
%)に、後述の5mm以上で分級して破砕した混練物を加
えた原料100重量部に対して、生石灰5.5重量部、
水30重量部を加え、フルード数1.1の中速で混練
し、得られた混練物をふるいで5mmにて分級して5mm以
上のものを破砕してから混練機に戻した後、5mm以下の
混練物を常温で1時間養生し、ついで、190℃にて1
0時間水熱処理を行って5mm以下の略球状の粒状体(黒
色)を製造した。この粒状体の吸水率は35%、陽イオ
ン交換容量は16meq/100g、圧壊強度は2.5kg
(2mm粒子)であり、溶出液pHは9.3であった。
EXAMPLES Example 1 Foundry sand dust A (SiO 2 : 65 wt%, plasticity limit: 32)
%), 5.5 parts by weight of quicklime, relative to 100 parts by weight of a raw material obtained by adding a kneaded material classified and crushed to a size of 5 mm to be described later,
Add 30 parts by weight of water, knead at a medium speed of Froude number 1.1, classify the resulting kneaded product by sieving at 5 mm, crush 5 mm or more, and then return to the kneading machine for 5 mm. The following kneaded product is aged at room temperature for 1 hour and then at 190 ° C for 1 hour.
Hydrothermal treatment was performed for 0 hours to produce substantially spherical particles (black) having a size of 5 mm or less. The water absorption rate of this granular material is 35%, the cation exchange capacity is 16 meq / 100g, and the crush strength is 2.5 kg.
(2 mm particles) and the pH of the eluate was 9.3.

【0031】実施例2 実施例1で得られた粒状体を0.1mmで分級し、0.1
mm以下の全量を鋳物砂ダストAに添加し、該ダスト10
0重量部に対して、生石灰5.5重量部、水31重量部
を加え、フルード数1.2の中速で混練を行った後、得
られた混練物を常温で0.5時間養生し、ついで、18
0℃にて10時間水熱処理を行って粒状固化体(灰色)
を製造した。この粒状体の吸水率は36%、陽イオン交
換容量は15meq/100g、圧壊強度は2.3kgであ
り、溶出液pHは9.2であった。
Example 2 The granules obtained in Example 1 were classified to 0.1 mm to give 0.1
The total amount of not more than mm is added to the foundry sand dust A, and the dust 10
5.5 parts by weight of quicklime and 31 parts by weight of water were added to 0 parts by weight, and the mixture was kneaded at a medium speed of Froude number of 1.2, and then the obtained kneaded product was aged at room temperature for 0.5 hours. , Then 18
Granulated solid (grey) after hydrothermal treatment at 0 ° C for 10 hours
Was manufactured. The granular material had a water absorption of 36%, a cation exchange capacity of 15 meq / 100 g, a crushing strength of 2.3 kg, and an eluent pH of 9.2.

【0032】実施例3 鋳物砂ダストB(SiO2:61wt%、塑性限界:35
%)100重量部に対して、生石灰6.5重量部、水3
4重量部を加え、フルード数0.8の中速で混練を行っ
た後、得られた混練物を常温で2時間養生し、ついで、
195℃にて10時間水熱処理を行って固化体を製造し
た。この固化体を衝撃式破砕機で破砕して10mm以下の
粒状体(灰色)とした。この粒状体の吸水率は37%、
陽イオン交換容量は23meq/100g、圧壊強度は2.
0kg(2mm粒子)であり、溶出液pHは9.6であった。
Example 3 Foundry sand dust B (SiO 2 : 61 wt%, plasticity limit: 35)
%) 6.5 parts by weight of quick lime and 3 parts of water with respect to 100 parts by weight
After adding 4 parts by weight and kneading at a medium speed of Froude number of 0.8, the resulting kneaded product was aged at room temperature for 2 hours, and then,
Hydrothermal treatment was performed at 195 ° C. for 10 hours to produce a solidified body. This solidified body was crushed by an impact crusher to obtain a granular body (gray) of 10 mm or less. The water absorption rate of this granular material is 37%,
Cation exchange capacity is 23meq / 100g, crushing strength is 2.
It was 0 kg (2 mm particles), and the pH of the eluate was 9.6.

【0033】実施例4 石炭灰(SiO2:55wt%、塑性限界:33%)10
0重量部に対して、消石灰10重量部、水35重量部を
加え、フルード数0.8の中速で混練を行った後、ブロ
ック状に振動成形し、得られた混練物を常温で2時間養
生し、ついで、180℃にて10時間水熱処理を行って
固化体を製造した。この固化体を衝撃式破砕機で破砕し
て40mm以下の粒状体(灰色)とした。この粒状体の圧
壊強度は20kg(10mm粒子)、修正CBRは75%で
あり、下層路盤材規格の20%を満足した。
Example 4 Coal ash (SiO 2 : 55 wt%, plasticity limit: 33%) 10
To 0 part by weight, 10 parts by weight of slaked lime and 35 parts by weight of water were added, and the mixture was kneaded at a medium speed of Froude number of 0.8, and then vibration-molded into a block shape. After curing for a period of time, hydrothermal treatment was performed at 180 ° C. for 10 hours to produce a solidified body. This solidified body was crushed by an impact crusher to give a granular body (gray) of 40 mm or less. The crushing strength of this granular material was 20 kg (10 mm particles) and the modified CBR was 75%, which satisfied the lower layer roadbed material standard of 20%.

【0034】実施例5 建設汚泥(水分50wt%、SiO2:53wt%(固形分
中)、塑性限界:48%)100重量部に対して、生石
灰20重量部を加え、フルード数0.8の中速で混練を
行った後、得られた混練物を60℃で1時間養生し、つ
いで、190℃にて10時間水熱処理を行って固化体を
製造した。この固化体を衝撃式破砕機で破砕して10mm
以下の粒状体(灰色)とした。この粒状体の吸水率は3
8%、陽イオン交換容量は14meq/100g、圧壊強度
は2.0kg(2mm粒子)であり、溶出液pHは9.4であ
った。
Example 5 20 parts by weight of quick lime was added to 100 parts by weight of construction sludge (water content: 50% by weight, SiO 2 : 53% by weight (in solid content), plasticity limit: 48%) to obtain a Froude number of 0.8. After kneading at a medium speed, the obtained kneaded product was aged at 60 ° C. for 1 hour, and then hydrothermally treated at 190 ° C. for 10 hours to produce a solidified product. This solidified body is crushed with an impact type crusher to 10 mm
The following granules (gray) were used. The water absorption of this granular material is 3
The cation exchange capacity was 8%, the cation exchange capacity was 14 meq / 100 g, the crush strength was 2.0 kg (2 mm particles), and the pH of the eluate was 9.4.

【0035】実施例6 鋳物砂ダストB100重量部に硝酸マグネシウム2重量
部、水25重量部を加え、混練を行った後、95℃にて
3時間加熱処理を行った。この処理物100重量部を用
いて、実施例2と同じ処理を行った。得られた粒状体
は、色がこげ茶色であり、吸水率は38%、陽イオン交
換容量は25meq/100g、圧壊強度は2.0kg(2mm
粒子)であり、溶出液pHは9.3であった。
Example 6 2 parts by weight of magnesium nitrate and 25 parts by weight of water were added to 100 parts by weight of casting sand dust B, and the mixture was kneaded and then heat-treated at 95 ° C. for 3 hours. The same treatment as in Example 2 was performed using 100 parts by weight of this treated product. The obtained granules were dark brown in color, had a water absorption rate of 38%, a cation exchange capacity of 25 meq / 100 g, and a crush strength of 2.0 kg (2 mm
Particles) and the pH of the eluate was 9.3.

【0036】比較例1 鋳物砂ダストB100重量部に対して、生石灰6.5重
量部、水24重量部を加え、フルード数3.5の高速で
混練を行った後、得られた混練物を常温で2時間養生
し、ついで、190℃にて10時間水熱処理を行って粒
状体(灰色)を製造した。この粒状体の吸水率は26
%、陽イオン交換容量は8meq/100g、圧壊強度は
0.5kg(2mm粒子)であり、溶出液pHは10.4であ
った。
Comparative Example 1 6.5 parts by weight of quick lime and 24 parts by weight of water were added to 100 parts by weight of casting sand dust B, and the mixture was kneaded at a high speed with a Froude number of 3.5. It was aged at room temperature for 2 hours and then hydrothermally treated at 190 ° C. for 10 hours to produce a granular body (gray). The water absorption rate of this granular material is 26.
%, The cation exchange capacity was 8 meq / 100 g, the crush strength was 0.5 kg (2 mm particles), and the pH of the eluate was 10.4.

【0037】比較例2 鋳物砂ダストB100重量部に対して、消石灰10重量
部、水32重量部を加え、フルード数3.5の高速で混
練を行った後、圧力300kg/cm2で押し出し成形を行
い、径20mm、長さ30〜60mmの円柱状に成形し、こ
れを常温で2時間養生し、ついで、200℃にて10時
間水熱処理を行って固化体(灰色)を製造した。この固
化体の修正CBRは15%であり、下層路盤材規格の2
0%を満足しなかった。
Comparative Example 2 10 parts by weight of slaked lime and 32 parts by weight of water were added to 100 parts by weight of casting sand dust B, and kneading was carried out at a high speed with a Froude number of 3.5, followed by extrusion molding at a pressure of 300 kg / cm 2. Was formed into a cylindrical shape having a diameter of 20 mm and a length of 30 to 60 mm, which was aged at room temperature for 2 hours and then hydrothermally treated at 200 ° C. for 10 hours to produce a solidified body (gray). The modified CBR of this solidified body is 15%, which is 2
0% was not satisfied.

【0038】[0038]

【発明の効果】本発明は上記のように構成されているの
で、つぎのような効果を奏する。 (1) 無機系廃棄物を水熱処理にて多孔質粒状体とす
るので、小さい環境負荷での処理技術により、無機系廃
棄物のリサイクルを図ることができる。 (2) 無機系廃棄物に石灰源材料を添加材として用
い、中速混練にて、ファニキュラーI、II状態〜キャピ
ラリー状態の混練物とすることにより、園芸材、土木
材、土壌改良材等に適した品質を有する多孔質粒状体が
製造できる。 (3) 混練物の3〜10mm以上を混練工程(又は原料
工程)に戻すこと、水熱処理後の0.1〜1mm以下の微
粉あるいは破砕後の0.05〜0.3mm以下の微粉を混
練工程(又は原料工程)に戻すことにより、製品の粒度
を確保し、廃棄物の全量を製品とすることができる。 (4) 酸化剤を用いることにより、粒状体の色の調整
を図ることができる。 (5) 石灰源材料、0.05〜0.3mm以下(又は
0.1〜1mm以下)の粉末量、水の量の調整により、泥
状廃棄物、粉末状廃棄物などの保有水分、塑性限界の異
なる廃棄物をファニキュラーI、II状態〜キャピラリー
状態の混練物とすることができ、粒状体又は固化体の品
質が確保できる。
Since the present invention is configured as described above, it has the following effects. (1) Since the inorganic waste is formed into a porous granular material by hydrothermal treatment, it is possible to recycle the inorganic waste by a processing technique with a small environmental load. (2) A horticultural material, earth and timber, a soil improving material, etc. by using a lime source material as an additive material to an inorganic waste and forming a kneaded material in a funicular I, II state to a capillary state by medium speed kneading. A porous granular material having a quality suitable for the above can be produced. (3) Returning 3 to 10 mm or more of the kneaded material to the kneading step (or raw material step), kneading 0.1 to 1 mm or less fine powder after hydrothermal treatment or 0.05 to 0.3 mm or less fine powder after crushing By returning to the process (or raw material process), the grain size of the product can be secured and the entire amount of waste can be made into the product. (4) The color of the granular material can be adjusted by using the oxidizing agent. (5) By adjusting the amount of lime source material, the powder amount of 0.05 to 0.3 mm or less (or 0.1 to 1 mm or less), and the amount of water, water content such as mud waste and powder waste, plasticity Wastes having different limits can be kneaded in the funicular I, II state to the capillary state, and the quality of the granular body or the solidified body can be secured.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の実施の第1形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程を示す概略説
明図である。
FIG. 1 is a schematic explanatory view showing steps of a method for producing a porous granular material using inorganic waste as a raw material according to the first embodiment of the present invention.

【図2】本発明の実施の第2形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程を示す概略説
明図である。
FIG. 2 is a schematic explanatory view showing steps of a method for producing a porous granular material using inorganic waste as a raw material according to the second embodiment of the present invention.

【図3】本発明の実施の第3形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程を示す概略説
明図である。
FIG. 3 is a schematic explanatory view showing steps of a method for producing a porous granular material using inorganic waste as a raw material according to the third embodiment of the present invention.

【図4】本発明の実施の第4形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程を示す概略説
明図である。
FIG. 4 is a schematic explanatory view showing steps of a method for producing a porous granular material using inorganic waste as a raw material according to the fourth embodiment of the present invention.

【図5】本発明の実施の第5形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程の一例を示す
概略説明図である。
FIG. 5 is a schematic explanatory view showing an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the fifth embodiment of the present invention.

【図6】本発明の実施の第6形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程の一例を示す
概略説明図である。
FIG. 6 is a schematic explanatory view showing an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the sixth embodiment of the present invention.

【図7】本発明の実施の第7形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程の一例を示す
概略説明図である。
FIG. 7 is a schematic explanatory view showing an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the seventh embodiment of the present invention.

【図8】本発明の実施の第8形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程の一例を示す
概略説明図である。
FIG. 8 is a schematic explanatory view showing an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the eighth embodiment of the present invention.

【図9】本発明の実施の第9形態による無機系廃棄物を
原料とする多孔質粒状体の製造方法の工程の一例を示す
概略説明図である。
FIG. 9 is a schematic explanatory view showing an example of steps of a method for producing a porous granular material using inorganic waste as a raw material according to the ninth embodiment of the present invention.

───────────────────────────────────────────────────── 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) B09B 3/00 C02F 11/00 101Z 4G012 C02F 11/00 101 C04B 28/18 ZAB 4H026 C04B 28/18 ZAB 40/02 4H061 40/02 C05D 3/00 C05D 3/00 3/04 3/04 C05F 7/00 C05F 7/00 C09K 17/02 H C09K 17/02 17/06 H 17/06 101:00 // C09K 101:00 B09B 3/00 304G Z Fターム(参考) 2B022 BA01 BA05 BB01 4D004 AA02 AA16 AA36 BA02 BA10 CA04 CA08 CA14 CA15 CA34 CC11 CC13 DA03 DA06 DA09 DA10 DA20 4D021 AB02 EA10 EB02 4D059 AA03 AA30 BG01 BJ01 BK08 BK09 BK11 CC04 CC10 DA04 DA05 DA66 DA70 4G004 AA02 4G012 MB04 PA25 PA26 PA28 PA30 PB07 PC01 PC11 PE04 PE07 RA03 RA05 RB03 4H026 AA03 AA04 AA05 AA18 AB04 4H061 AA02 CC02 CC03 CC08 CC14 CC51 DD20 EE41 FF08 FF21 GG13 GG42 GG70 LL02 LL05 LL15 LL24 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) B09B 3/00 C02F 11/00 101Z 4G012 C02F 11/00 101 C04B 28/18 ZAB 4H026 C04B 28/18 ZAB 40 / 02 4H061 40/02 C05D 3/00 C05D 3/00 3/04 3/04 C05F 7/00 C05F 7/00 C09K 17/02 H C09K 17/02 17/06 H 17/06 101: 00 // C09K 101: 00 B09B 3/00 304G Z F term (reference) 2B022 BA01 BA05 BB01 4D004 AA02 AA16 AA36 BA02 BA10 CA04 CA08 CA14 CA15 CA34 CC11 CC13 DA03 DA06 DA09 DA10 DA20 4D021 AB02 EA10 CC09 BK01 BB01 BB01 BB01 DA04 DA05 DA66 DA70 4G004 AA02 4G012 MB04 PA25 PA26 PA28 PA30 PB07 PC01 PC11 PE04 PE07 RA03 RA05 RB03 4H026 AA03 AA04 AA05 AA18 AB04 4H 061 AA02 CC02 CC03 CC08 CC14 CC51 DD20 EE41 FF08 FF21 GG13 GG42 GG70 LL02 LL05 LL15 LL24

Claims (11)

【特許請求の範囲】[Claims] 【請求項1】 原料である無機系廃棄物100重量部
に、石灰源材料2.5〜25重量部及び必要に応じて水
0.01〜30重量部を加えて混練機に投入し、フルー
ド数が0.1〜2.0となるように中速で混練を行って
含水率20%以上のファニキュラーI状態の略球状に造
粒された混練物とし、該混練物を3〜10mmで分級し
て、3〜10mm以上のものは破砕処理した後、前記混練
機又は投入原料に戻し、3〜10mm以下のものを常温〜
95℃で0.2〜36時間養生を行った後、130〜2
20℃で1〜24時間水熱処理を行って粒状体とするこ
とを特徴とする無機系廃棄物を原料とする多孔質粒状体
の製造方法。
1. To 100 parts by weight of an inorganic waste as a raw material, 2.5 to 25 parts by weight of a lime source material and 0.01 to 30 parts by weight of water as necessary are added and charged into a kneading machine to obtain a fluid. Kneading is carried out at a medium speed so that the number becomes 0.1 to 2.0 to obtain a substantially spherical granulated kneaded product in the funicular I state having a water content of 20% or more, and the kneaded product is 3 to 10 mm. After classifying, 3 to 10 mm or more is crushed, and then returned to the kneader or the input material, and 3 to 10 mm or less at room temperature to
After curing at 95 ° C for 0.2 to 36 hours, 130 to 2
A method for producing a porous granular material using an inorganic waste as a raw material, which comprises hydrothermal treatment at 20 ° C. for 1 to 24 hours to obtain a granular material.
【請求項2】 水熱処理で得られた粒状体を0.1〜1
mmで分級し、0.1〜1mm以下のものを混練機又は投入
原料に戻し、0.1〜1mm以上の粒状体を得る請求項1
記載の無機系廃棄物を原料とする多孔質粒状体の製造方
法。
2. The granular material obtained by hydrothermal treatment is 0.1 to 1
3. Classifying in mm, returning 0.1 to 1 mm or less to a kneader or charging material to obtain granules of 0.1 to 1 mm or more.
A method for producing a porous granular material using the described inorganic waste as a raw material.
【請求項3】 原料である無機系廃棄物100重量部
に、石灰源材料2.5〜25重量部及び必要に応じて水
0.01〜60重量部を加えて混練機に投入し、フルー
ド数が0.1〜2.0となるように中速で混練を行って
含水率30%以上のファニキュラーII状態乃至キャピラ
リー状態の混練物とし、該混練物を常温〜95℃で0.
2〜36時間養生を行い、ついで、130〜220℃で
1〜24時間水熱処理を行った後、破砕処理を行って粒
状体を得ることを特徴とする無機系廃棄物を原料とする
多孔質粒状体の製造方法。
3. To 100 parts by weight of the inorganic waste as a raw material, 2.5 to 25 parts by weight of the lime source material and 0.01 to 60 parts by weight of water as necessary are added and charged into a kneading machine to obtain a fluid. The mixture is kneaded at a medium speed so that the number becomes 0.1 to 2.0 to obtain a kneaded product in a funicular II state or a capillary state having a water content of 30% or more, and the kneaded product is from room temperature to 95 ° C. at 0.
Curing for 2-36 hours and then hydrothermal treatment at 130-220 ° C. for 1-24 hours, followed by crushing treatment to obtain granules, porous material made from inorganic waste Granular body manufacturing method.
【請求項4】 原料である無機系廃棄物100重量部
に、石灰源材料2.5〜25重量部及び必要に応じて水
0.01〜60重量部を加えて混練機に投入し、フルー
ド数が0.1〜2.0となるように中速で混練を行って
含水率30%以上のファニキュラーII状態乃至キャピラ
リー状態の混練物とし、該混練物を振動成形した後、常
温〜95℃で0.2〜36時間養生を行い、ついで、1
30〜220℃で1〜24時間水熱処理を行った後、破
砕処理を行って粒状体を得ることを特徴とする無機系廃
棄物を原料とする多孔質粒状体の製造方法。
4. To 100 parts by weight of the inorganic waste as a raw material, 2.5 to 25 parts by weight of the lime source material and 0.01 to 60 parts by weight of water as necessary are added, and the mixture is put into a kneading machine, and then the fluid is added. The mixture is kneaded at a medium speed so that the number becomes 0.1 to 2.0 to give a kneaded product in a funicular II state or a capillary state having a water content of 30% or more, and the kneaded product is subjected to vibration molding, and then at room temperature to 95%. Curing for 0.2 to 36 hours at ℃, then 1
A method for producing a porous granular material using an inorganic waste as a raw material, which comprises performing a hydrothermal treatment at 30 to 220 ° C. for 1 to 24 hours and then performing a crushing treatment to obtain a granular material.
【請求項5】 前処理として、無機系廃棄物100重量
部に、酸化剤0.5〜20重量部及び必要に応じて水
0.01〜60重量部を加えて混練し、得られた混練物
を常温〜220℃で0.2〜15時間加熱処理又は水熱
処理した後、得られた処理物に石灰源材料及び必要に応
じて水を加えて請求項1〜4のいずれかに記載の処理を
行うことを特徴とする無機系廃棄物を原料とする多孔質
粒状体の製造方法。
5. As a pretreatment, 100 parts by weight of the inorganic waste is added with 0.5 to 20 parts by weight of an oxidizer and 0.01 to 60 parts by weight of water if necessary, and the mixture is kneaded. The lime source material and water as needed are added to the obtained processed material after heat-treating or hydrothermally treating the material for 0.2 to 15 hours at room temperature to 220 ° C., and then the method according to claim 1. A method for producing a porous granular material using an inorganic waste as a raw material, characterized by performing a treatment.
【請求項6】 原料である無機系廃棄物100重量部
に、石灰源材料2.5〜25重量部、酸化剤0.5〜2
0重量部、及び必要に応じて水0.01〜60重量部を
加えて混練機に投入し、フルード数が0.1〜2.0と
なるように中速で混練を行って含水率30%以上のファ
ニキュラーII状態乃至キャピラリー状態の混練物とし、
該混練物に対して請求項3記載の養生、水熱処理、破砕
処理、又は請求項4記載の振動成形、養生、水熱処理、
破砕処理を行って粒状体を得ることを特徴とする無機系
廃棄物を原料とする多孔質粒状体の製造方法。
6. 100 parts by weight of inorganic waste as a raw material, 2.5 to 25 parts by weight of a lime source material, and 0.5 to 2 parts of an oxidizer.
0 part by weight, and 0.01 to 60 parts by weight of water as necessary are added to the kneader and kneaded at a medium speed so that the Froude number is 0.1 to 2.0, and the water content is 30. % Or more of the kneaded material in the funicular II state or the capillary state,
Curing, hydrothermal treatment, crushing treatment according to claim 3, or vibration molding, curing, hydrothermal treatment according to claim 4 to the kneaded product,
A method for producing a porous granular material using an inorganic waste as a raw material, characterized by crushing a granular material.
【請求項7】 無機系廃棄物を破砕した後、請求項1〜
6のいずれかに記載の処理を行うことを特徴とする無機
系廃棄物を原料とする多孔質粒状体の製造方法。
7. The method according to claim 1 after crushing the inorganic waste.
7. The method for producing a porous granular material using an inorganic waste as a raw material, which comprises performing the treatment according to any one of 6 above.
【請求項8】 無機系廃棄物を0.05〜0.3mmで分
級を行って粗粒子の除去を行い、微粒子は請求項1〜7
のいずれかに記載の処理を行い、粗粒子は水熱処理後の
処理物と混合することを特徴とする無機系廃棄物を原料
とする多孔質粒状体の製造方法。
8. Inorganic waste is classified at 0.05 to 0.3 mm to remove coarse particles, and fine particles as claimed in claim 1 to 7.
The method for producing a porous granular material using an inorganic waste as a raw material, characterized in that the coarse particle is mixed with a treated product after hydrothermal treatment.
【請求項9】 水熱処理し破砕した後の粒状体を0.0
5〜0.3mmで分級して微粒子の除去を行い、微粒子を
投入原料又は混練機に戻して請求項3〜8のいずれかに
記載の処理を行うことを特徴とする無機系廃棄物を原料
とする多孔質粒状体の製造方法。
9. The granular material after hydrothermal treatment and crushing is 0.0
Fine particles are removed by classification with 5 to 0.3 mm, and the fine particles are returned to a charging raw material or a kneader to perform the treatment according to any one of claims 3 to 8 as a raw material. And a method for producing a porous granular material.
【請求項10】 無機系廃棄物が、鋳物砂ダスト、砕石
スラッジ、建設汚泥、上水汚泥及び石炭灰の少なくとも
いずれかである請求項1〜9のいずれかに記載の無機系
廃棄物を原料とする多孔質粒状体の製造方法。
10. The inorganic waste according to claim 1, wherein the inorganic waste is at least one of foundry sand dust, crushed stone sludge, construction sludge, tap water sludge and coal ash. And a method for producing a porous granular material.
【請求項11】 石灰源材料として、生石灰、消石灰、
セメント、スラグ粉末及び廃コンクリート微粉の少なく
ともいずれかを用いる請求項1〜10のいずれかに記載
の無機系廃棄物を原料とする多孔質粒状体の製造方法。
11. Quick lime, slaked lime, as a lime source material,
The method for producing a porous granular body using an inorganic waste as a raw material according to claim 1, wherein at least one of cement, slag powder and waste concrete fine powder is used.
JP2002044252A 2002-02-21 2002-02-21 Method for producing porous granular material using inorganic waste as raw material Expired - Fee Related JP3628661B2 (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005138073A (en) * 2003-11-10 2005-06-02 Kawasaki Heavy Ind Ltd Solid obtained by stabilizing waste
JP2005253313A (en) * 2004-03-09 2005-09-22 Kawasaki Heavy Ind Ltd Greening material composition using waste as raw material and greening material using the same
JP2007268513A (en) * 2006-03-06 2007-10-18 Kobe Steel Ltd Method for treating waste

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102077745A (en) * 2009-11-26 2011-06-01 廖晓康 Dendrobium bonsai manufactured by planting dendrobium on stone or tree stump

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005138073A (en) * 2003-11-10 2005-06-02 Kawasaki Heavy Ind Ltd Solid obtained by stabilizing waste
JP2005253313A (en) * 2004-03-09 2005-09-22 Kawasaki Heavy Ind Ltd Greening material composition using waste as raw material and greening material using the same
JP4610912B2 (en) * 2004-03-09 2011-01-12 カワサキプラントシステムズ株式会社 Greening material composition using waste as a raw material and greening material using the same
JP2007268513A (en) * 2006-03-06 2007-10-18 Kobe Steel Ltd Method for treating waste

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