JP2001115158A - Production method of granular soil using molten slag of refuse - Google Patents

Production method of granular soil using molten slag of refuse

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Publication number
JP2001115158A
JP2001115158A JP29427999A JP29427999A JP2001115158A JP 2001115158 A JP2001115158 A JP 2001115158A JP 29427999 A JP29427999 A JP 29427999A JP 29427999 A JP29427999 A JP 29427999A JP 2001115158 A JP2001115158 A JP 2001115158A
Authority
JP
Japan
Prior art keywords
soil
molten slag
water
granular
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
JP29427999A
Other languages
Japanese (ja)
Inventor
Shigenori Yamada
惠規 山田
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP29427999A priority Critical patent/JP2001115158A/en
Publication of JP2001115158A publication Critical patent/JP2001115158A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To provide a method for producing regenerated granular soil from a molten slag of refuse occurring from an ash melting and solidifying facility. SOLUTION: Incineration ash of refuse is melted, then solidified, and granulated.; the resultant molten slag in an amount of about 20 wt.% is mixed under stirring with a water-containing soil occurring at construction sites or civil work sites to give a mixed soil which can be easily granulated; and the mixed soil is further mixed under stirring with a carboxyl-group-containing water-soluble polymer to be granulated and then is treated with a solidifying 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、ゴミ焼却灰を溶融
炉内で溶融処理したときに多量に発生するゴミの溶融ス
ラグの再利用に関する。更に詳細に言えば、ゴミの溶融
スラグを建設及び土木工事等に伴って発生する含水土壌
に混合し粒状固化させてなるゴミの溶融スラグを用いた
粒状土の製造方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the reuse of molten slag of refuse generated in large quantities when refuse incineration ash is melted in a melting furnace. More specifically, the present invention relates to a method of manufacturing granular soil using molten slag of garbage obtained by mixing molten slag of garbage with water-containing soil generated during construction and civil engineering and solidifying the mixture.

【0002】[0002]

【従来の技術】家庭や商店、事務所等で発生したゴミ
は、一般廃棄物としてゴミ収集車で収集され清掃工場に
搬送される。清掃工場では収集したゴミを一般ゴミと不
燃粗大ゴミに分離、区分した後、それぞれ専用のゴミ焼
却施設で焼却処理される。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が、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。
2. Description of the Related Art Garbage generated in homes, shops, offices and the like is collected as general waste by a garbage truck and transported to a cleaning plant. The garbage collection plant separates and separates the collected garbage into general garbage and non-combustible bulky garbage, and then incinerates them at dedicated garbage incineration facilities. A large amount of incineration ash is generated from the incineration facility during the incineration treatment, and this incineration ash contains a large amount of harmful substances such as dioxins and highly toxic and hardly decomposable compounds.

【0003】そこで、この焼却灰からこれらの有害物質
を削減するため、及び焼却灰の絶対量を削減するため、
焼却灰を灰溶融固化施設で約1200度以上の超高温で
溶融処理することが一部の清掃工場で実施されている。
この溶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るため、許容
範囲内の数値の有害検出物を含有する暗黒色のガラス状
の固形物が発生する。ゴミの「溶融スラグ」とは、この
ガラス状の固形物を細かく砕いて粒子化した固化物粒子
の総称である。
In order to reduce these harmful substances from the incinerated ash and to reduce the absolute amount of the incinerated ash,
Melting of incinerated ash at an ultra-high temperature of about 1200 ° C. or more in an ash fusion solidification facility is being carried out at some of the cleaning plants.
The organic matter in the incineration ash is completely burned by this melting process,
In addition, since harmful substances are completely gasified and diffused, a dark black glassy solid containing harmful substances having a numerical value within an allowable range is generated. The “molten slag” of garbage is a general term for solidified particles obtained by finely crushing and solidifying the glassy solid.

【0004】従来、ゴミの溶融スラグは、再資源化物質
として、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。
[0004] Conventionally, attempts have been made to use molten slag of garbage as a recycled material as a substitute for materials such as concrete blocks for construction and natural aggregates. (1.88 mm), it cannot be compacted and is therefore not suitable for backfilling, etc., and is currently transported as general waste to final disposal sites for landfill disposal.

【0005】[0005]

【発明が解決しようとする課題】ところで、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、焼却灰中の有害物質の早急な除去対策が求めら
れ、これを受け、全国の地方自治体の清掃工場に溶融固
化施設の併設や新設等の計画が進められている。このた
め、今後、各地方自治体の清掃工場から多量のゴミ溶融
スラグの発生が避けられない状況になっているが、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
溶融スラグの再資源としての活用策が期待されている。
By the way, harmful compounds such as dioxin in incineration ash generated from garbage incinerators have been widely recognized as highly carcinogenic environmental pollutants, and harmful substances in incineration ash have been recognized. As a result, urgent removal measures have been demanded, and in response to this, plans are underway to install smelting and solidification facilities at municipal waste management plants nationwide and to establish new facilities. For this reason, it is inevitable that a large amount of waste slag will be generated from waste management plants in each local government.However, in the Tokyo metropolitan area and other local governments, final disposal sites as landfill disposal Since there is a limit in securing the molten slag, it is expected to utilize the molten slag as a resource.

【0006】[0006]

【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、ゴミの溶融スラグの物性を活用すべく鋭意
研究した結果、該溶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、該溶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、建設工事や
土木工事等で発生する含水土壌とゴミの焼却灰を溶融し
た後、これを固化、かつ粒子化してなる溶融スラグとを
あらかじめ混合した後、カルボキシル基含有水溶性重合
体と混合し、更に石灰等の固化材で処理してなるゴミの
溶融スラグを用いた粒状土の製造方法を特徴とする。
SUMMARY OF THE INVENTION The present invention has been made in view of the above-mentioned circumstances, and as a result of intensive research on utilizing the physical properties of molten slag of garbage, the molten slag has been applied to hydrous soil generated from a construction site or the like. It has been found that when mixed, the fine particles of the molten slag combine with the particles of the hydrous soil to transform the highly viscous hydrous soil into finely granular hydrous soil. More specifically, the present invention melts hydrated soil and garbage incineration ash generated in construction work, civil engineering work, etc., solidifies this, and mixes in advance with molten slag obtained by granulation, and then forms a carboxyl group. The method is characterized by a method for producing granular soil using molten slag of refuse obtained by mixing with a group-containing water-soluble polymer and further treating with a solidifying material such as lime.

【0007】[0007]

【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溶融スラグは、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、灰溶融固化施設
の電気溶融炉内で約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溶融化物
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, the incinerated ash generated from the refuse incineration facility is refined, and then 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.

【0008】このようにして得たゴミの溶融スラグは、
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。この溶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
る含水土壌は、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。
[0008] 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. The molten slag is stirred and mixed with hydrous soil generated during construction work and 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 which are generated with general civil engineering and construction work such as building construction work, residential land development work, underground pipe work, and the like. be able to.

【0009】本発明は、溶融スラグを含水土壌に添加し
て撹拌機で撹拌混合する。溶融スラグを含水土壌に添加
して撹拌混合すると、溶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、含水土壌は溶融スラグを含んだ粒状化しやすい混合
土に変性する。
In the present invention, molten slag is added to hydrous soil and mixed with a stirrer. When the molten slag is added to the hydrous soil and agitated and mixed, the finely solidified granules constituting the molten slag are combined with the soil particles of the crushed hydrous soil, so that the hydrous soil is easily mixed into granules containing the molten slag. Transforms to soil.

【0010】溶融スラグを含水土壌に添加する割合は、
約20重量%程度が好ましい。混合の割合が20重量%
を越えると、撹拌混合しても溶融スラグが塊として残存
し、含水土壌と溶融スラグとの結合性が生じない。この
ため、溶融スラグは、含水性を有さない細かい固化粒状
物の状態で含水土壌中に残存するため、後述するカルボ
ルキシル基水溶性重合体と混合しても溶融スラグと反応
しないので、粒状土を生成することができない。
[0010] The rate of adding molten slag to hydrous soil is as follows:
About 20% by weight is preferred. Mixing ratio is 20% by weight
If it exceeds, the molten slag remains as a lump even after stirring and mixing, and the bonding property between the hydrated soil and the molten slag does not occur. For this reason, the molten slag remains in the hydrated soil in the form of fine solid granules having no hydration, and does not react with the molten slag even when mixed with the carboxyl-based water-soluble polymer described below. Cannot be generated.

【0011】本発明に使用する水溶性重合体は、100
mlの水に通常0.5g以上溶解する重合体である。該重
合体は、親水基としてカルボキシル基を有するものであ
り、重合体を構成する全単量体単位のうちカルボルキシ
ル基を有する単量体が、通常1〜80モル%、好ましく
は5〜60モル%含まれる。また、カルボキシル基は、
遊離酸または塩の形のどちらで存在してもよい。塩の種
類としては、例えばナトリウム、カリウムなどのアルカ
リ金属の塩、カルシウム、マグネシウムなどのアルカリ
土類金属の塩、アンモニウム塩、炭素数1〜18のアル
キルアミン、アルカノールアミンなどのアミン塩、およ
びこれら2種以上の混合物があるが、好ましくはアルカ
リ金属の塩類である。
The water-soluble polymer used in the present invention is 100
It is a polymer that usually dissolves 0.5 g or more in ml of water. The polymer has a carboxyl group as a hydrophilic group, and a monomer having a carboxyl group is usually 1 to 80 mol%, preferably 5 to 60 mol, of all monomer units constituting the polymer. %included. Also, the carboxyl group is
It may be present in either the free acid or salt form. Examples of the type of salt include salts of alkali metals such as sodium and potassium, salts of alkaline earth metals such as calcium and magnesium, ammonium salts, amine salts such as alkylamines having 1 to 18 carbon atoms, alkanolamines, and the like. There is a mixture of two or more, but preferably salts of alkali metals.

【0012】かかる水溶性重合体としては、(メタ)ア
クリル酸またはその塩と(メタ)アクリルアミドとの共
重合体、マレイン酸またはその塩と酢酸ビニルとの共重
合体、イタコン酸またはその塩と(メタ)アクリルアミ
ドとの共重合体などの合成水溶性重合体、アラビヤガ
ム、カラヤガム、トラントガム、アルギン酸などの天然
水溶性重合体、及び、カルボキシメチルセルロース、カ
ルボキシハイドロエチルセルロース、グアーガム変性物
のような半合成水溶性重合体が例示される。
Examples of such a water-soluble polymer include a copolymer of (meth) acrylic acid or a salt thereof and (meth) acrylamide, a copolymer of maleic acid or a salt thereof and vinyl acetate, and a copolymer of itaconic acid or a salt thereof. Synthetic water-soluble polymers such as copolymers with (meth) acrylamide, natural water-soluble polymers such as arabic gum, karaya gum, tranto gum, alginic acid, and semi-synthetic water-soluble polymers such as carboxymethylcellulose, carboxyhydroethylcellulose, and modified guar gum Examples of the polymer are:

【0013】以上のカルボキシル基含有水溶性重合体の
うち、好ましくは(メタ)アクリル酸またはその塩と
(メタ)アクリルアミドとの共重合体である。(メタ)
アクリル酸またはその塩を含有する(メタ)アクリルア
ミド系重合体としては、(メタ)アクリル酸またはその
塩と(メタ)アクリルアミドを共重合したもののほか、
(メタ)アクリルアミドの単独重合体を部分加水分解し
たものでもよい。
Among the above water-soluble polymers containing a carboxyl group, a copolymer of (meth) acrylic acid or a salt thereof and (meth) acrylamide is preferred. (Meta)
Examples of the (meth) acrylamide-based polymer containing acrylic acid or a salt thereof include those obtained by copolymerizing (meth) acrylic acid or a salt thereof and (meth) acrylamide,
(Meth) acrylamide homopolymer may be partially hydrolyzed.

【0014】更に、以上のカルボキシル基含有水溶性重
合体には、親水性基としてスルホン酸基を含む単量体、
例えばビニルスルホン酸、アクリルスルホン酸、2−ア
クリルアミド−2−メチルプロパンスルホン酸およびこ
れらの塩などを含めて共重合してもよい。また、水溶性
を阻害しない程度であればオレフィン、アクリル酸エス
テル、ビニルエステルのような疎水性単量体を含んでも
よい。
Further, the above-mentioned carboxyl group-containing water-soluble polymer includes a monomer containing a sulfonic acid group as a hydrophilic group,
For example, copolymerization may be carried out including vinyl sulfonic acid, acrylic sulfonic acid, 2-acrylamido-2-methylpropane sulfonic acid and salts thereof. Further, a hydrophobic monomer such as an olefin, an acrylate or a vinyl ester may be contained as long as it does not inhibit water solubility.

【0015】カルボキシル基含有水溶性重合体の添加量
は、溶融スラグの混合割合や含水土壌の含水比などに応
じて異なるが、溶融スラグを約20重量%を混合した含
水土壌からなる被処理原料の場合は、被処理原料に対し
て0.07〜0.1重量%である。また、カルボキシル
基含有水溶性重合体と被処理原料との撹拌混合は、撹拌
機を用いて緩やかな撹拌を通常0.8〜2分程度行うの
が望ましい。
The amount of the water-soluble polymer containing a carboxyl group varies depending on the mixing ratio of the molten slag, the water content of the water-containing soil, and the like. Is 0.07 to 0.1% by weight based on the raw material to be treated. In addition, the stirring and mixing of the carboxyl group-containing water-soluble polymer and the raw material to be treated are preferably performed with gentle stirring using a stirrer, usually for about 0.8 to 2 minutes.

【0016】被処理原料にカルボキシル基含有水溶性重
合体を上記の割合で添加し、撹拌機で約50秒以上緩や
かに撹拌混合すると、カルボキシル基含有水溶性重合体
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を吸引して溶解す
る。このため、カルボキシル基含有水溶性重合体に吸引
された土壌内部の水分は、遊離水としての性質を失い、
疑似固定水(吸着水)として粒状土の表面に固定される
ことになり、粒状土は互いに付着せず、撹拌混合される
ことにより、球状に造粒される。
When the carboxyl group-containing water-soluble polymer is added to the raw material to be treated in the above ratio and gently stirred and mixed for about 50 seconds or more with a stirrer, the carboxyl group-containing water-soluble polymer makes the surface of the granular soil uniform. After coating, the free water between the soil particles inside the granular soil and the solid particles of the molten slag is sucked and dissolved. Therefore, the water inside the soil sucked by the carboxyl group-containing water-soluble polymer loses its properties as free water,
It is fixed on the surface of the granular soil as pseudo-fixed water (adsorbed water), and the granular soil does not adhere to each other, and is granulated into a sphere by stirring and mixing.

【0017】本発明は、生成された粒状土の表面に固定
された被膜を安定化させ、長期に亘って粒状に保持する
ため、石灰等の固化材を粒状土の表面に均一に付着させ
る。本発明に使用する固形材は、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。
According to the present invention, a solidified material such as lime is uniformly adhered to the surface of the granular soil in order to stabilize the film fixed on the surface of the generated granular soil and maintain the coating in a granular form for a long period of time. The solid 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. The 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, etc. can be applied, but dehydration and solidification Fast lime powder is preferred. The amount of solidified material
It is 0.2 to 20% by weight, preferably 0.5 to 20% by weight, based on the raw material to be treated.

【0018】水分を吸引し溶解したカルボキシル基含有
水溶性重合体の被膜で被覆された粒状土の表面に、生石
灰等の固化材が付着すると、被膜中の水分は固形材と反
応して発熱しながら消石灰となるため、被膜中の水分を
蒸発させながら、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、強度が発現する。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 a solidified material such as quicklime adheres to the surface of the granular soil coated with a water-soluble polymer film containing a carboxyl group that has been sucked and dissolved, the water in the film reacts with the solid material to generate heat. Since the slaked lime is formed, the water develops in the film by evaporating the water and penetrating from the surface with a high lime distribution, and the pozzolanic reaction develops the strength. 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.

【0019】本発明の製造方法により製造された粒状土
においては、粒度0.075〜1.18mmの範囲内にあ
る短い平均粒径を有するゴミの溶融スラグの固化粒状物
が、含水土壌を構成する土粒子と結合するため、生成さ
れた粒状土の粒度は、0.425〜9.50mmの範囲内
にあって、東京都の基準である13.0mm以下の要件を
満たし、且つ粒径も幅広く均衡が保たれるため、従来の
粒状改良土と同等の地盤支持力、強度特性、粒土特性を
有し透水性に優れた粒状土を得ることができる。
In the granular soil produced by the production method of the present invention, the solidified granular material of the molten slag of garbage having a short average particle size in the range of 0.075 to 1.18 mm constitutes the hydrous soil. The particle size of the generated granular soil is in the range of 0.425 to 9.50 mm to meet the requirement of 13.0 mm or less which is the standard of Tokyo, and the particle size is also Since the equilibrium is maintained widely, it is possible to obtain a granular soil having excellent ground permeability, strength characteristics, and granular soil characteristics equivalent to those of the conventional granular improved soil.

【0020】[0020]

【実施例】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、灰溶融固化施設の
電気溶融炉内で約1200度以上の超高温の条件下で加
熱燃焼して得た溶融化物を、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
溶融スラグを調製した。
EXAMPLES 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 incineration 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 was cooled and solidified in a cooling treatment facility. The dark 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.

【0021】調製された溶融スラグを、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0.075〜1.18mm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。また、平均粒径が0.68mm
であった。なお、該溶融スラグの粒度分布測定試験結果
を粒土分布曲線として図1に示す。
The prepared molten slag was put into 0.075 mm,
Examination of the granular soil with each of the 1.18 mm and 2.36 mm sieve testers shows that particles having a cumulative ratio of about 90% to 0.45 to 1.18 mm within the range of 0.075 to 1.18 mm. Accounted for more than%. The average particle size is 0.68 mm
Met. The results of the particle size distribution measurement test of the molten slag are shown in FIG. 1 as a grain distribution curve.

【0022】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と上記溶融スラグ
1.0kg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、上記工程で得た粒状土にアクリルアミドとアクリル
酸ナトリウムの共重合体6g(被処理原料に対して0.
1重量%)を添加し約90秒間緩やかに撹拌混合した
後、生石灰粉末180g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0.425〜9.50mm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。得た粒状土の粒度分
布測定試験結果を粒土分布曲線として図2に示す。
On the other hand, a water content of 98%
5 kg of hydrous soil mainly composed of Kanto loam and 1.0 kg of the above-mentioned molten slag were put into a mixer having a capacity of 20 liters and stirred and mixed for about 60 seconds to obtain a mixed soil which was easily granulated. Next, 6 g of a copolymer of acrylamide and sodium acrylate was added to the granular soil obtained in the above step (0.
1% by weight) and gently stirring and mixing for about 90 seconds, then adding 180 g of quicklime powder and stirring for 30 seconds with little external pressure to obtain granular soil coated with slaked lime. When this granular soil is subjected to a sieve tester of 0.075 mm, 1.18 mm, and 2.36 mm to measure the particle size and the like, the particle size is in the range of 0.425 to 9.50 mm,
The accumulation rate was small, medium, and large, and the particle size was widely balanced. The average particle size was 2.3 mm. The results of the particle size distribution measurement test of the obtained granular soil are shown in FIG. 2 as a granular soil distribution curve.

【0023】このように調製した粒状土の粒度は、上記
したように東京都基準(粒度13.0mm以下)に適合
し、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、溶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 conformed to the Tokyo Metropolitan Standard (particle size of 13.0 mm or less) as described above, and had the same particle size and particle size distribution as high quality sand. In addition, the ground support and shear strength characteristics were equivalent to those of the conventional granular improved soil. Furthermore, 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 water after water permeation, and no separation of molten slag was recognized.

【0024】比較例 実施例で入手したゴミの溶融スラグを単独で、締め固め
材として使用したが、平均粒径数値が、0.68mmと細
かく、また累積率で、0.45〜01.180mm迄の粒
子が90%以上を占めるため、締め固めすることができ
なかった。また、水浸すると溶融スラグが溶解した黒く
濁った水が出た。
Comparative Example The molten slag of garbage obtained in the examples was used alone as a compacting material, but the average particle size was as fine as 0.68 mm, and the cumulative ratio was 0.45 to 01.180 mm. Since the particles up to 90% or more accounted for 90% of the particles, they could not be compacted. Further, upon immersion in water, black turbid water in which the molten slag was dissolved came out.

【0025】[0025]

【発明の効果】本発明によれば、予め、含水土壌とゴミ
の溶融スラグとを混合しているので、含水土壌は添加さ
れた溶融スラグの粒子を含んだ細かい粒状の含水土壌に
なるため、カルボルキシル基含有水溶性重合体の浸透が
良好になり、生成された粒状土はより川砂に近いものと
なる。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、溶融スラグを添加することにより、溶融ス
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 the garbage are mixed in advance, the hydrated soil becomes a fine granular hydrated soil containing the particles of the added molten slag. The penetration of the carboxyl group-containing water-soluble polymer is improved, and the resulting granular soil becomes closer to river sand. In addition, it was difficult to stir a highly viscous hydrous soil, but by adding 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.

【0026】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溶融スラグを再生
粒状土の再生資源として利用できるため、溶融スラグの
利用性を高め、環境問題に貢献するところが大きい。ま
た、溶融スラグを再生利用するにあたり、溶融スラグ自
体に特別な加工処理工程を介在する必要がなく、灰溶融
固化施設で発生した溶融スラグを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。
Further, since the molten slag of garbage, which has been mostly landfilled as landfill waste, can now be used as a recycled resource for reclaimed granular soil, the utilization of the molten slag is enhanced, contributing to environmental problems. large. Further, when recycling the molten slag, it is not necessary to intervene a special processing step in the molten slag itself, and the molten slag generated in the ash fusion solidification facility can be used as it is, so that the cost required for the recycling processing can be reduced.

【0027】また、粒状土は、溶融スラグの暗黒色にな
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。
Further, the granular soil does not become dark black of the molten slag and has almost the same color as ordinary soil. Therefore, even if it is not subjected to coloring treatment, it can be used as grass soil, groundwork, or sand of bunker. Can be used.

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

【図1】溶融スラグの粒土分布曲線を示す。FIG. 1 shows a grain distribution curve of molten slag.

【図2】実施例1により得た粒状土の粒土分布曲線を示
す。
FIG. 2 shows a granular soil distribution curve of the granular soil obtained in Example 1.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 ゴミの焼却灰を溶融した後、これを固
化、かつ粒子化してなる溶融スラグと含水土壌とを混合
した後、カルボキシル基含有水溶性重合体を混合し、更
に石灰等の固化材で処理してなるゴミの溶融スラグを用
いた粒状土の製造方法。
After melting the incinerated ash of garbage, solidifying it and mixing the molten slag formed into particles with water-containing soil, mixing the carboxyl group-containing water-soluble polymer, and further solidifying lime etc. A method for producing granular soil using molten slag of garbage treated with wood.
【請求項2】 前記含水土壌に前記溶融スラグを20重
量%混合したことを特徴とする請求項1に記載のゴミの
溶融スラグを用いた粒状土の製造方法。
2. The method according to claim 1, wherein the molten slag is mixed with the hydrated soil in an amount of 20% by weight.
JP29427999A 1999-10-15 1999-10-15 Production method of granular soil using molten slag of refuse Pending JP2001115158A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP29427999A JP2001115158A (en) 1999-10-15 1999-10-15 Production method of granular soil using molten slag of refuse

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29427999A JP2001115158A (en) 1999-10-15 1999-10-15 Production method of granular soil using molten slag of refuse

Publications (1)

Publication Number Publication Date
JP2001115158A true JP2001115158A (en) 2001-04-24

Family

ID=17805659

Family Applications (1)

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

Country Link
JP (1) JP2001115158A (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61205646A (en) * 1985-03-11 1986-09-11 大同特殊鋼株式会社 Manufacture of aggregate for public construction
JPH0617052A (en) * 1992-06-29 1994-01-25 Tokyo Kankyo Service Kk Method for amending water-containing soil
JPH07246396A (en) * 1994-03-10 1995-09-26 Mitsubishi Materials Corp Treatment of dredging slurry
JPH105800A (en) * 1996-06-21 1998-01-13 Chichibu Onoda Cement Corp Dehydration treating material for sludge and dehydration treatment
JPH1045458A (en) * 1996-08-01 1998-02-17 Kyuichi Maruyama Production of self-packing concrete
JPH1130008A (en) * 1996-12-04 1999-02-02 Kubota Corp Method for using molten slag as construction mixing material and manufacture of cement construction material and wall material

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61205646A (en) * 1985-03-11 1986-09-11 大同特殊鋼株式会社 Manufacture of aggregate for public construction
JPH0617052A (en) * 1992-06-29 1994-01-25 Tokyo Kankyo Service Kk Method for amending water-containing soil
JPH07246396A (en) * 1994-03-10 1995-09-26 Mitsubishi Materials Corp Treatment of dredging slurry
JPH105800A (en) * 1996-06-21 1998-01-13 Chichibu Onoda Cement Corp Dehydration treating material for sludge and dehydration treatment
JPH1045458A (en) * 1996-08-01 1998-02-17 Kyuichi Maruyama Production of self-packing concrete
JPH1130008A (en) * 1996-12-04 1999-02-02 Kubota Corp Method for using molten slag as construction mixing material and manufacture of cement construction material and wall material

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