JP2001292634A - Method for producing improved soil by using liquid slag of waste - Google Patents

Method for producing improved soil by using liquid slag of waste

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Publication number
JP2001292634A
JP2001292634A JP2000109176A JP2000109176A JP2001292634A JP 2001292634 A JP2001292634 A JP 2001292634A JP 2000109176 A JP2000109176 A JP 2000109176A JP 2000109176 A JP2000109176 A JP 2000109176A JP 2001292634 A JP2001292634 A JP 2001292634A
Authority
JP
Japan
Prior art keywords
soil
molten slag
waste
ash
garbage
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2000109176A
Other languages
Japanese (ja)
Inventor
Hideji Komine
秀治 小峰
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.)
Individual
Original Assignee
Individual
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Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP2000109176A priority Critical patent/JP2001292634A/en
Publication of JP2001292634A publication Critical patent/JP2001292634A/en
Pending legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for producing improved soil obtained by improving water-containing soil formed in the sites of civil engineering and construction by using a molten slag of a waste formed in ash-melting and solidifying facilities and direct melting facilities. SOLUTION: The molten slag obtained by melting the burned ash of the waste, solidifying the melted ash, and granulating the solidified ash, in an amount of about 20 wt.% is mixed and stirred with the water-containing soil formed in the construction site and the civil engineering site to provide a mixed soil which can be easily granulated, and the resultant mixed soil is treated with a solidification material such as lime.

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、ゴミやゴミの焼却
灰を熔融炉内で熔融処理したときに多量に発生するゴミ
の熔融スラグを用いて土木建築現場で発生する含水土壌
を改良した改良土の製造方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an improvement in which water-containing soil generated at a civil engineering construction site is improved by using molten slag generated in a large amount when refuse or incinerated ash of refuse is melted in a melting furnace. It relates to a method for producing soil.

【0002】[0002]

【従来の技術】従来、土木建築現場から発生する残土の
ほとんどは含水性土壌であるため、再利用できずに埋め
立て処分したり他の場所へ搬出・廃棄されているが、環
境への影響が問題になってきている。このため、土木建
築現場から発生する残土の再利用として、比較的含水比
の低い粘土が余り高くない含水土壌を対象に、生石灰を
用いた残土処理方法が、特開昭54−121086号、
特開平4−345685号、特開平8−73852号、
特開平8−41460号、及び特開平8−48975号
として開発されている。
2. Description of the Related Art Conventionally, most of the residual soil generated from civil engineering construction sites is hydrous soil, so it cannot be reused and is landfilled or transported to other places for disposal. Is becoming a problem. For this reason, as a method for reusing the remaining soil generated from a civil engineering construction site, a method for treating the remaining soil using quicklime for a water-bearing soil in which the clay having a relatively low water content is not so high is disclosed in JP-A-54-121086.
JP-A-4-345885, JP-A-8-73852,
It has been developed as JP-A-8-41460 and JP-A-8-48975.

【0003】一方、家庭や商店、事務所等で発生したゴ
ミは、清掃工場のゴミ焼却施設で焼却処理されるが、こ
の焼却処理に伴って焼却施設から多量の焼却灰が発生す
る。この焼却灰には、ダイオキシン類を始めとする、毒
性が強く分解されにくい化合物等の有害物質が多く含ま
れている。そこで、この焼却灰からこれらの有害物質を
削減すると共に、焼却灰の絶対量を減少するため、ゴミ
や焼却灰を更に灰熔融固化施設で約1200度以上の超
高温条件下で熔融処理することが一部の清掃工場で実施
されている。
On the other hand, garbage generated in homes, shops, offices, and the like is incinerated in a garbage incineration facility of a waste cleaning plant, and a large amount of incineration ash is generated from the incineration facility along with the incineration processing. This incinerated ash contains a large amount of harmful substances such as dioxins and compounds that are highly toxic and hardly decomposed. Therefore, in order to reduce these harmful substances from the incinerated ash and to reduce the absolute amount of the incinerated ash, the garbage and incinerated ash should be further melted in an ash melting and solidification facility under ultra-high temperature conditions of about 1200 degrees or more. Has been implemented in some waste treatment plants.

【0004】この熔融処理により焼却灰中の有機物は完
全に燃焼し、また有害物質も完全にガス化して放散さ
れ、許容範囲内の数値の有害検出物を含有する熔融化し
た無機物が発生する。本発明の「ゴミの熔融スラグ」と
は、このように、一般廃棄物及び産業廃棄物を直接熔融
化した無機物並びに一般廃棄物及び産業廃棄物の焼却灰
を熔融化した無機物を、冷却処理施設で冷却固化して得
た暗黒色のガラス状の固化物を細かく砕いて粒子化した
粒子状固化物を言う。
[0004] By this melting treatment, organic substances in the incineration ash are completely burned, and harmful substances are completely gasified and dissipated, thereby generating molten inorganic substances containing harmful substances having a numerical value within an allowable range. The `` molten slag of garbage '' of the present invention refers to an inorganic substance obtained by directly melting general waste and industrial waste and an inorganic substance obtained by melting incinerated ash of general waste and industrial waste in a cooling treatment facility. Refers to a particulate solidified product obtained by finely crushing a dark black glassy solidified product obtained by cooling and solidifying in step.

【0005】ところで、近年、ゴミ焼却炉より発生する
焼却灰中のダイオキシン等の有害化合物は、発ガン性の
高い環境汚染物質として広く認識されるに至り、全国の
地方自治体の清掃工場に熔融固化施設の併設や新設等の
計画が進められており、今後、各地方自治体の清掃工場
から多量のゴミ熔融スラグの発生が避けられない状況に
なっている。このため、ゴミの熔融スラグの再資源化物
質に関しては、建築用コンクリートブロック、自然骨材
等の材料の代替品等に使用する試みが行われている。
In recent years, harmful compounds such as dioxins in incineration ash generated from refuse incinerators have been widely recognized as highly carcinogenic environmental pollutants. Plans are underway to add and install facilities, and it is inevitable that a large amount of garbage-melting slag will be generated from waste management plants in each local government. For this reason, attempts have been made to use recycled materials from molten slag of garbage as substitutes for materials such as concrete blocks for construction and natural aggregates.

【0006】[0006]

【発明が解決しようとする課題】しかし、ゴミの熔融ス
ラグの粒度が、単粒度(0.0075〜1.18mm)の
ため締め固めができず、このため、埋め戻し材等には適
さないので大部分は一般廃棄物として最終処分場に搬送
され埋め立て廃棄処分されているのが現状である。しか
し、首都圏を始めとして、各地方自治体においては、埋
め立て廃棄処分としての最終処分場の確保に限界がある
ため、該熔融スラグの再資源としての活用策が期待され
ている。
However, since the particle size of the molten slag of the refuse is a single particle size (0.0075 to 1.18 mm), it cannot be compacted and is not suitable for backfilling materials. At present, most of them are transported to final disposal sites as general waste and landfilled. However, in each local government, including the Tokyo metropolitan area, there is a limit in securing a final disposal site for landfill disposal, and thus there is an expectation for measures to utilize the molten slag as a resource.

【0007】また、従来の土木建築工事に伴って発生す
る残土に生石灰を添加混合してなる残土の処理法では、
混合機などに土塊が付着し易く処理が困難であると共
に、無理やり処理をしても強度向上が望めず、再生土と
しての歩留まりが悪い問題があった。このため、土木建
築現場から発生する含水性のある残土を再資源として活
用できる改良策が求められていた。
[0007] In addition, in the conventional method for treating residual soil obtained by adding and mixing quicklime to residual soil generated during civil engineering and construction work,
There is a problem that the soil mass easily adheres to the mixing machine or the like and the treatment is difficult, and even if the treatment is forcibly performed, the strength cannot be expected to be improved, and the yield as the reclaimed soil is poor. For this reason, there has been a demand for an improvement measure that can utilize the water-containing residual soil generated from a civil engineering construction site as a resource.

【0008】[0008]

【課題を解決するための手段】本発明は、上記のような
状況に鑑み、ゴミの熔融スラグの物性を活用すべく鋭意
研究した結果、該熔融スラグを建設工事現場等から発生
する含水土壌に混合すると、該熔融スラグの細かい粒子
が含水土壌の粒子と結合して、粘性の強い含水土壌を細
かい粒の含水土壌に変性することを見い出してなされた
ものである。具体的に述べると、本発明は、含水土壌
と、固化・粒子化してなるゴミの熔融スラグとの混合物
に、石灰等の固化材を加え撹拌することを特徴とする。
SUMMARY OF THE INVENTION The present invention has been made in view of the above-mentioned situation, and as a result of intensive studies to utilize the physical properties of molten slag of garbage, the molten slag has been applied to hydrous soil generated from construction sites and the like. It has been found that upon mixing, the fine particles of the molten slag combine with the particles of the hydrous soil to transform the highly viscous hydrous soil into fine-grained hydrous soil. More specifically, the present invention is characterized in that a solidifying material such as lime is added to a mixture of water-containing soil and molten slag of solidified / particulated garbage and stirred.

【0009】[0009]

【発明の実施の形態】以下、本発明を詳細に説明する。
本発明に利用するゴミの熔融スラグは、以下に述べる処
理工程を経て入手することができる。先ず、ゴミ焼却施
設から発生した焼却灰を細粒化した後、灰熔融固化施設
の電気熔融炉内で約1200度以上の超高温の条件下で
加熱燃焼させる。この加熱燃焼により発生した熔融化物
を、冷却処理施設で冷却固化し、生成された暗黒色のガ
ラス状の固形物を磁選機にかけて金属片を除去した後、
破砕処理機で破砕して粒子化する。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail.
The molten slag of refuse used in the present invention can be obtained through the following processing steps. First, after the incinerated ash generated from the refuse incineration facility is refined, it is heated and burned in an electric melting furnace of the ash melting and solidifying facility at an ultra-high temperature of about 1200 degrees or more. The molten material generated by this heating and combustion is cooled and solidified in a cooling treatment facility, and the generated dark black glassy solid is subjected to a magnetic separator to remove metal pieces.
It is crushed into particles by a crusher.

【0010】このようにして得たゴミの熔融スラグは、
粒度が0.075〜1.18mm範囲内で、平均粒経数値
が0.68mm前後の粒径の小さい撥水性のあるガラス状
の固化粒状物である。この熔融スラグを建設工事等に伴
って発生した含水土壌と撹拌混合する。本発明に使用す
る含水土壌として、ビル建設工事、宅地造成工事、地中
埋設管工事等の一般の土木・建築工事に伴って発生する
柔軟または粘着性の強い建設発生土、建設残土を使用す
ることができる。
The molten slag of garbage thus obtained is
This is a water-repellent glassy solidified particle having a small particle size with a particle size in the range of 0.075 to 1.18 mm and an average particle size of about 0.68 mm. This molten slag is stirred and mixed with hydrous soil generated during construction work or the like. As the hydrous soil used in the present invention, use is made of a soft or highly sticky construction generated soil and construction residual soil generated with general civil engineering and building work such as building construction work, residential land development work, underground pipe work, and the like. be able to.

【0011】本発明は、ゴミの熔融スラグを含水土壌に
添加して撹拌機で撹拌混合する。ゴミの熔融スラグを含
水土壌に添加して撹拌混合すると、ゴミの熔融スラグを
構成する細かい固化粒状物は、解砕された含水土壌の土
粒子と結合するため、含水土壌は熔融スラグを含んだ粒
状化しやすい粒状土に変性する。
In the present invention, molten slag of garbage is added to hydrous soil and mixed with a stirrer. When the molten slag of garbage is added to the hydrous soil and agitated and mixed, the finely solidified granules constituting the molten slag of garbage combine with the ground particles of the crushed hydrous soil, so that the hydrous soil contains the molten slag. It transforms into granular soil that is easily granulated.

【0012】熔融スラグを含水土壌に添加する割合は、
10〜30%重量程度が好ましい。混合の割合が30%
重量を越えると、撹拌混合しても熔融スラグが塊として
残存するため、含水土壌と熔融スラグとの結合性が生じ
ず、熔融スラグは、含水性を帯びない細かい固化粒状物
の状態で含水土壌中に残存する。このため、後述する生
石灰等の固化材を加えて撹拌しても熔融スラグと反応し
ないので、粒状土を生成することができない。
[0012] The ratio of adding molten slag to hydrous soil is as follows:
About 10 to 30% by weight is preferable. 30% mixing ratio
If the weight is exceeded, the molten slag remains as a lump even after stirring and mixing, so that the binding between the hydrous soil and the molten slag does not occur, and the molten slag is in the form of fine solid granules that do not have hydrous properties. Remains inside. For this reason, even if a solidifying material such as quick lime described later is added and stirred, it does not react with the molten slag, so that granular soil cannot be generated.

【0013】本発明に使用する固化材は、粒状土の表面
に付着し易いものがよく、平均粒径がは0.5mm以下の
石灰粉末を用いるのが好ましい。固化材としての石灰に
は、酸化カルシウム、水酸化カルシウムを含むもので、
具体的には、消石灰、生石灰、水硬セメント、石灰系改
良材、セメント系改良材などを適用できるが、脱水およ
び固化速度が速い生石灰の粉末が好ましい。固化材の添
加量は、被処理原料に対して、0.2〜20重量%であ
り、好ましくは0.5〜20重量%である。
The solidified material used in the present invention is preferably one that easily adheres to the surface of the granular soil, and it is preferable to use lime powder having an average particle size of 0.5 mm or less. Lime as a solidifying material contains calcium oxide and calcium hydroxide.
Specifically, slaked lime, quicklime, hydraulic cement, lime-based improving material, cement-based improving material, and the like can be applied, but quicklime powder having a high dehydration and solidification rate is preferable. The addition amount of the solidifying material is 0.2 to 20% by weight, preferably 0.5 to 20% by weight, based on the raw material to be treated.

【0014】熔融スラグを含水土壌に添加して撹拌混合
した混合物に、上記の割合で固化材、例えば生石灰、を
添加し撹拌混合すると、該生石灰は、粒状土の表面を均
一に被覆し、粒状土内部の土粒子や溶融スラグの固形粒
子間の遊離水分と反応し発熱しながら消石灰となり、遊
離水分は蒸発し、石灰分布の高い表面から浸透しつつポ
ゾラン反応によって、粒状土の表面に固定されて、互い
に付着しない強度の優れた粒状土が生成される。なお、
粒状土の強度を更に発現させるために養生を行うことも
できる。養生は、通常、常温下で1〜7日、好ましくは
3〜6日程度放置することで行う。
When the solidified material, for example, quicklime, is added to the mixture obtained by adding the molten slag to the water-containing soil and stirring and mixing, and then stirring and mixing, the quicklime uniformly covers the surface of the granular soil, It reacts with the free water between the soil particles in the soil and solid particles of the molten slag to generate heat and becomes slaked lime, and the free water evaporates and is fixed to the surface of the granular soil by the pozzolanic reaction while penetrating from the surface with high lime distribution. As a result, a granular soil having excellent strength that does not adhere to each other is generated. In addition,
Curing can be performed to further develop the strength of the granular soil. Curing is usually carried out by leaving at room temperature for 1 to 7 days, preferably about 3 to 6 days.

【0015】以下、本発明の具体例として、若干の実施
例を述べるが本発明はこれら実施例に限定されるもので
ない。 実施例 ゴミ焼却施設から発生した焼却灰を、灰熔融固化施設の
電気熔融炉内で約1200度以上の超高温の条件下で加
熱燃焼して得た熔融化物を、冷却処理施設で冷却固化し
た暗黒色のガラス状の固形物を、磁選機にかけ金属片を
除去した後、破砕処理機で破砕して固形粒状化のゴミの
熔融スラグを調製した。調製された熔融スラグを、0.
075mm、1.18mm及び2.36mmの各ふるいわけ試
験器により粒土を調査すると、粒度0.075〜1.1
8mmの範囲内に、累積率で、0.45〜1.18mmまで
の粒子が約90%以上を占めていた。
Hereinafter, some examples will be described as specific examples of the present invention, but the present invention is not limited to these examples. Example The incinerated ash generated from a garbage incineration facility was heated and burned in an electric melting furnace of an ash fusion and solidification facility under an ultra-high temperature condition of about 1200 ° C. or more, and then cooled and solidified in a cooling treatment facility. The dark black glassy solid was subjected to a magnetic separator to remove metal pieces, and then crushed by a crusher to prepare a molten slag of solid granulated garbage. The prepared molten slag was used for 0.1 g.
Examination of the granular soil with a sieve tester of 075 mm, 1.18 mm and 2.36 mm revealed a grain size of 0.075 to 1.1.
Within the range of 8 mm, particles with a cumulative rate of 0.45 to 1.18 mm accounted for about 90% or more.

【0016】一方、建築現場から採取した含水比98%
の関東ロームが主体な含水土壌5kgと上記熔融スラグ
0.5〜1.5kgとを容量20リットルのミキサーに
入れて約60秒間撹拌混合して粒状化しやすい混合土を
得た。次に、上記工程で得た混合物に生石灰粉末180
gを添加し、更に30秒間ほとんど外圧を加えないで撹
拌すると消石灰で被覆された粒状土を得た。この粒状土
を0.075mm、1.18mm、及び2.36mmのふるい
わけ試験器にかけ粒径等を計測すると、粒度は0.42
5〜9.50mmに範囲内であり、累積率は小、中、大に
亘って粒径も幅広く均衡が保たれ、平均粒径は2.3mm
であった。
On the other hand, a water content of 98% collected from a building site
5 kg of hydrous soil mainly composed of Kanto loam and 0.5 to 1.5 kg of the above-mentioned molten slag were put into a 20-liter mixer and stirred and mixed for about 60 seconds to obtain a mixed soil which was easily granulated. Next, quick lime powder 180 was added to the mixture obtained in the above step.
g was further added and the mixture was stirred for 30 seconds with little external pressure, to obtain granular soil coated with slaked lime. The granular soil was measured using a sieve tester of 0.075 mm, 1.18 mm, and 2.36 mm to measure the particle size and the like.
5 to 9.50 mm, the accumulation rate is small, medium, and large, and the particle size is widely balanced. The average particle size is 2.3 mm.
Met.

【0017】このように調製した粒状土の粒度は、良質
な砂と同等の粒径、粒度分布を有していた。また、従来
の粒状改良土と同等の地盤支持力、せん断強度特性を備
えていた。更に雨水等によっても柔らかにならず、川砂
と同等の良好な透水性を備え、透水後の水には濁りが見
られず、熔融スラグの分離は全く認められなかった。
The particle size of the granular soil thus prepared had a particle size and a particle size distribution equivalent to those of good-quality sand. In addition, the ground support and shear strength characteristics were equivalent to those of the conventional granular improved soil. Further, it did not become soft even by rainwater or the like, had good water permeability equivalent to river sand, did not show any turbidity in the water after water permeation, and no separation of the molten slag was observed.

【0018】[0018]

【発明の効果】本発明によれば、予め、含水土壌とゴミ
の熔融スラグとを混合しているので、含水土壌は添加さ
れた熔融スラグの粒子を含んだ細かい粒状土となり、且
つその表面は、固化材で被覆されているため、生成され
た粒状土は強度の優れたより川砂に近いものを得ること
ができる。また、粘性が強い含水土壌は、撹拌するのが
困難であったが、熔融スラグを添加することにより、熔
融スラグが撹拌補助剤的な役割を果たすため、撹拌機に
対する負荷を軽減でき耐久性を向上することができる。
According to the present invention, since the hydrated soil and the molten slag of garbage are mixed in advance, the hydrated soil becomes fine granular soil containing the particles of the added molten slag, and the surface thereof is formed. Since it is covered with the solidified material, the generated granular soil can be obtained with excellent strength and closer to river sand. In addition, it was difficult to stir the highly viscous hydrous soil, but by adding the molten slag, the molten slag plays a role as a stirring aid, so the load on the stirrer can be reduced and the durability can be reduced. Can be improved.

【0019】また、従来、その大部分が埋め立て廃棄物
として埋め立て処理されていたゴミの熔融スラグや土木
建築現場の残土を、改良土の再生資源として利用できる
ため、熔融スラグ、含水土壌の利用性を高め、環境問題
に貢献するところが大きい。また、熔融スラグや土木建
築現場の含水土壌を再生利用するにあたり、特別な加工
処理工程を介在する必要がなく、そのまま利用できるの
で再生処理に要する費用を軽減できる。
In addition, since the molten slag of garbage and the remaining soil of civil engineering construction sites, most of which have been conventionally landfilled as landfill waste, can be used as recycled resources for improved soil, the availability of molten slag and hydrous soil can be improved. And contribute to environmental issues. Further, when recycling the molten slag and the water-containing soil at the construction site, there is no need to intervene a special processing step, and the recycled slag can be used as it is, so that the cost required for the recycling processing can be reduced.

【0020】また、粒状土は、暗黒色にならず、通常の
土とほぼ同等の色であるため、着色処理を施さなくて
も、芝の目土や下地、バンカーの砂としても使用するこ
とができる。
Since the granular soil does not become dark black and has almost the same color as ordinary soil, it can be used as grass soil, groundwork, or sand of a bunker without coloring treatment. Can be.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 含水土壌と、固化・粒子化してなるゴミ
の熔融スラグとの混合物に、石灰等の固化材を加え撹拌
することを特徴とするゴミの熔融スラグを用いた改良土
の製造方法。
1. A method for producing an improved soil using a molten slag of garbage, wherein a solidifying material such as lime is added to a mixture of a hydrous soil and a molten slag of garbage solidified and granulated, and the mixture is stirred. .
【請求項2】 前記含水土壌に前記熔融スラグを10〜
30%重量の割合で混合したことを特徴とする請求項1
に記載のゴミの熔融スラグを用いた改良土の製造方法。
2. The molten slag is added to the water-containing soil in an amount of 10 to 10.
2. The mixture according to claim 1, wherein the mixture is 30% by weight.
A method for producing improved soil using a molten slag of garbage as described in 1 above.
JP2000109176A 2000-04-11 2000-04-11 Method for producing improved soil by using liquid slag of waste Pending JP2001292634A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000109176A JP2001292634A (en) 2000-04-11 2000-04-11 Method for producing improved soil by using liquid slag of waste

Publications (1)

Publication Number Publication Date
JP2001292634A true JP2001292634A (en) 2001-10-23

Family

ID=18621900

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2001292634A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006326446A (en) * 2005-05-25 2006-12-07 Nippon Steel Corp Construction sludge improvement method and improvement system used for it
JP2011177112A (en) * 2010-03-01 2011-09-15 Nippon Steel Engineering Co Ltd Material for promoting growth of turf, and method for growing turf

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006326446A (en) * 2005-05-25 2006-12-07 Nippon Steel Corp Construction sludge improvement method and improvement system used for it
JP4632865B2 (en) * 2005-05-25 2011-02-16 新日本製鐵株式会社 Construction sludge improvement method and improvement equipment used therefor
JP2011177112A (en) * 2010-03-01 2011-09-15 Nippon Steel Engineering Co Ltd Material for promoting growth of turf, and method for growing turf

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