JPH11209189A - Production of water clarifying material by recycling incineration ash as valuable resource - Google Patents

Production of water clarifying material by recycling incineration ash as valuable resource

Info

Publication number
JPH11209189A
JPH11209189A JP10009181A JP918198A JPH11209189A JP H11209189 A JPH11209189 A JP H11209189A JP 10009181 A JP10009181 A JP 10009181A JP 918198 A JP918198 A JP 918198A JP H11209189 A JPH11209189 A JP H11209189A
Authority
JP
Japan
Prior art keywords
water
glaze
valuable resource
incinerated ash
proper
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
JP10009181A
Other languages
Japanese (ja)
Inventor
Shuichi Sugita
秀一 杉田
Takeo Hayashi
健夫 林
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 JP10009181A priority Critical patent/JPH11209189A/en
Priority to TW87120112A priority patent/TW434200B/en
Publication of JPH11209189A publication Critical patent/JPH11209189A/en
Pending legal-status Critical Current

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  • Compositions Of Oxide Ceramics (AREA)
  • Processing Of Solid Wastes (AREA)
  • Physical Water Treatments (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a manufacturing method of a water clarifying material by which large amount of the incineration ashes can be utilized as valuable resources. SOLUTION: Incineration ash of municipal refuse is mixed with mineral clay for ceramic raw material at a proper ratio, the mixture is molded to a proper shape, the molding is fused and calcined at a proper temp. to form a pottery base material 2. Then a glaze is applied to the pottery base material 2 and is calcined again at a proper temp. The glaze contains mineral powder having stretching vibrations or deformation vibrations exhibiting maximum molecular vibration spectrum in an infrared wavelength region among molecular vibration spectra of water.

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、焼却灰、特に都市
ごみ焼却灰の再利用技術に係り、焼却灰を有価資源化し
た水浄化材の製造方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a technology for recycling incinerated ash, particularly municipal refuse incinerated ash, and to a method for producing a water purification material using incinerated ash as a valuable resource.

【0002】[0002]

【従来の技術】都市ごみ焼却施設から排出する焼却灰
は、重金属や多くの有害物質を含んでいる。このため
に、焼却灰をそのままに再利用することは困難であり、
現状においては主に埋立処分を行なっている。
2. Description of the Related Art Incineration ash discharged from municipal solid waste incineration facilities contains heavy metals and many harmful substances. For this reason, it is difficult to reuse incinerated ash as it is,
At present, landfills are mainly conducted.

【0003】[0003]

【発明が解決しようとする課題】しかし、近年において
は、埋立処分場を新たに確保することは環境保全の立場
から困難になっている、このために、焼却灰を有価資源
として再利用することが求められており、歩道の舗装を
行なうインターブロック等の原料として利用するなどの
限られた用途に利用されているに過ぎないものである。
However, in recent years, it has become difficult to secure a new landfill site from the standpoint of environmental protection. For this reason, it is necessary to reuse incinerated ash as a valuable resource. And are used only for limited applications such as being used as a raw material for interblocks and the like for paving sidewalks.

【0004】本発明は、焼却灰を大量に有価資源として
利用することができる焼却灰を有価資源化した水浄化材
の製造方法を提供することを目的とする。
[0004] It is an object of the present invention to provide a method for producing a water purification material in which incinerated ash can be used as a valuable resource in which the incinerated ash can be used as a valuable resource.

【0005】[0005]

【課題を解決するための手段】上記した課題を解決する
ために、本発明の焼却灰を有価資源化した水浄化材の製
造方法は、都市ごみ焼却灰と窯業原料用鉱物粘土とを適
当比の割合で混合して後に適当形状に造型し、この造型
物を適当温度で溶融焼成して陶器基材を形成し、陶器基
材に釉薬を塗布して再び適当温度で焼成するものであっ
て、釉薬が、水の分子振動スペクトルの内で、赤外線の
波長領域において最大の分子振動スペクトルを発する伸
縮振動または変角振動を持つ鉱物の粉体を含む構成とし
たものである。
Means for Solving the Problems In order to solve the above-mentioned problems, a method for producing a water purifying material using incinerated ash as a valuable resource according to the present invention comprises an appropriate ratio of municipal waste incinerated ash to mineral clay for ceramic raw materials. And then molded into an appropriate shape, melt molded and fired at an appropriate temperature to form a ceramic substrate, apply a glaze to the ceramic substrate, and fire again at an appropriate temperature. The glaze is configured to include a mineral powder having a stretching vibration or a bending vibration that emits the maximum molecular vibration spectrum in the infrared wavelength region in the molecular vibration spectrum of water.

【0006】[0006]

【発明の実施の形態】本発明の実施形態を図面に基づい
て説明する。図1〜図2において、水浄化材1は、陶器
基材2と釉薬部3とからなる。陶器基材2は、水浄化材
1の核になる部分であり、都市ごみ焼却灰と窯業原料用
鉱物粘土とを1:5の割合で混合した混合原料を、粒状
に造粒するなどして適当形状に造型し、この造型物を1
200℃〜1300℃の適当温度で溶融焼成したもので
ある。都市焼却灰は、飛灰を除いた下灰を有価資源とし
て再利用するものであり、窯業原料鉱物粘土としては、
窯業用石英粉、アルミナ粉等である。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the present invention will be described with reference to the drawings. In FIG. 1 and FIG. 2, the water purification material 1 includes a ceramic base material 2 and a glaze portion 3. The pottery base material 2 is a core part of the water purification material 1. The mixed raw material obtained by mixing the municipal waste incineration ash and the mineral clay for the ceramic raw material at a ratio of 1: 5 is granulated into granules. Mold into an appropriate shape,
It is obtained by melting and firing at an appropriate temperature of 200 ° C to 1300 ° C. Urban incineration ash is used to reuse the bottom ash excluding fly ash as a valuable resource.
Quartz powder and alumina powder for ceramics.

【0007】次に、釉薬部3は、陶器基材2に釉薬を塗
布して再び1300℃前後の適当温度で焼成して成形す
るものであって、釉薬として窯業用の釉薬に、水の分子
振動スペクトルの内で、赤外線の波長領域において最大
の分子振動スペクトルを発する伸縮振動または変角振動
を持つ鉱物の粉体を含んでいる。
[0007] The glaze section 3 is for applying a glaze to the ceramic substrate 2 and firing it again at an appropriate temperature of about 1300 ° C to form a glaze. In the vibration spectrum, it includes a mineral powder having a stretching vibration or a bending vibration that emits the maximum molecular vibration spectrum in the infrared wavelength region.

【0008】この鉱物について説明する。各種の鉱石
は、その成分に起因して固有の分子振動スペクトルを持
つことはよく知られている。鉱石固有の分子振動スペク
トルが水の分子振動スペクトルに等しければその振動は
共鳴する。このため、採取した鉱石を400℃〜850
℃程度で焼成して脱水後に再結晶化したものを200〜
450メッシュ程度に粉砕した物を使う。通常は、焼成
後粉砕するが、粉砕後焼成して使用しても構わない。
[0008] This mineral will be described. It is well known that various ores have a unique molecular vibration spectrum due to their components. If the molecular vibration spectrum of the ore is equal to the molecular vibration spectrum of water, the vibration resonates. For this reason, the collected ore is stored at 400 ° C. to 850
What was recrystallized after dehydration after firing at about
Use a material crushed to about 450 mesh. Usually, it is pulverized after firing, but may be used after firing.

【0009】また、窯業用の釉薬としては、例えばSr
O,TiO2,CoO,FeO,Fe23等がある。配
合は、鉱物成分90〜95重量%と釉薬成分5〜10重
量%とするか、場合によっては、鉱物成分80〜95重
量%と釉薬成分5〜20重量%とする。
As a glaze for the ceramic industry, for example, Sr
O, TiO 2 , CoO, FeO, Fe 2 O 3 and the like. The composition is 90 to 95% by weight of the mineral component and 5 to 10% by weight of the glaze component, or 80 to 95% by weight of the mineral component and 5 to 20% by weight of the glaze component depending on the case.

【0010】以下、上記した構成における作用を説明す
る。焼却灰は、重金属や有害物質を含むものであるが、
1200〜1300℃の温度において2回の焼成を行な
うことにより、焼却灰が溶融してガラス化し、ガラス状
分子構造の中に有害物質や重金属を取り込むので、有害
物質の溶出が起こらず、陶器基材2の原料として有価資
源となる。
The operation of the above configuration will be described below. Incinerated ash contains heavy metals and harmful substances,
By performing the firing twice at a temperature of 1200 to 1300 ° C., the incinerated ash is melted and vitrified, and harmful substances and heavy metals are incorporated into the glassy molecular structure. It is a valuable resource as a raw material for the material 2.

【0011】水浄化材1の使用においては、例えば球状
に形成した複数の水浄化材1をメッシュ状のケーシング
4内に内包し、水路等に浸漬する。この状態で、水浄化
材1は、釉薬部3から赤外線の波長領域において最大の
分子振動スペクトルを発し、周囲の水の酸化還元電位を
減少させる。つまり、親水性の岩石の結晶において励起
する内部振動の振動エネルギーを、励起移動、特に共鳴
伝達により水分子およびオキソニウムに伝達して電子を
励起し、その後に起こる励起状態から基底状態への遷
移、および分解により派生する水和電子によって、還元
力の強い水質の水を造ることができる。この酸化還元電
位の減少がもたらす効果の一例を以下に説明する。
When the water purifying material 1 is used, for example, a plurality of spherical water purifying materials 1 are contained in a mesh casing 4 and immersed in a water channel or the like. In this state, the water purifying material 1 emits the maximum molecular vibration spectrum in the infrared wavelength region from the glaze portion 3 and reduces the oxidation-reduction potential of the surrounding water. In other words, the vibrational energy of internal vibrations excited in the crystal of the hydrophilic rock is transferred to water molecules and oxonium by excitation transfer, especially resonance transfer, to excite electrons, and the subsequent transition from the excited state to the ground state, And hydration electrons derived from the decomposition make it possible to produce water having a high reducing power. An example of the effect of the reduction of the oxidation-reduction potential will be described below.

【0012】水道水中にはトリハロメタンの前駆物質を
なす天然の有機物が微量に存在し、この前駆物質が塩素
と反応してトリハロメタンを生成する。この前駆物質の
代表的なものは、フミン酸やフルボ酸などの天然の腐食
物質であり、水中の色度成分と呼ばれるものである。フ
ミン酸粒子はタンパク質の回りを水の層が3重に取り囲
んだものであるが、最外層の水から順次に還元性を強め
て行くことによってタンパク質表面の水が薄層となり、
微生物との接触が促進され、微生物により分解される。
[0012] Tap water contains trace amounts of natural organic substances that are precursors of trihalomethane, and this precursor reacts with chlorine to produce trihalomethane. Typical of these precursors are natural corrosive substances such as humic acid and fulvic acid, which are called chromatic components in water. Humic acid particles are three layers of water surrounding the protein, but the water on the protein surface becomes a thin layer by increasing the reducibility sequentially from the outermost layer of water,
Contact with microorganisms is promoted and decomposed by microorganisms.

【0013】したがって、フミン酸を含んだ水道水を流
水状態で水浄化材1に接触させると、水自体の還元力の
高まりによってフミン酸を取り囲む水分子の層の薄層化
を図ることができ、結果としてトリハロメタンの前駆物
資の除去を促進することができる。
Therefore, when the tap water containing humic acid is brought into contact with the water purifying material 1 in a flowing state, the reducing power of the water itself increases the thickness of the water molecules surrounding the humic acid. As a result, the removal of the precursor material of trihalomethane can be promoted.

【0014】また、一般細菌に対しては、その生存に必
要なミネラル分、有機質等の栄養分を還元力により低減
するとともに、水の酸化還元電位の低減により気体中の
酸素の溶解度を高め、酸素分子が還元されて水分子を生
成するまでに発生する中間体の毒性により、殺菌作用を
及ぼすことができる。
With respect to general bacteria, minerals and nutrients such as organic substances necessary for their survival are reduced by reducing power, and the solubility of oxygen in gas is increased by reducing the oxidation-reduction potential of water. The toxic effects of the intermediates generated before the molecule is reduced to form a water molecule can exert a bactericidal action.

【0015】つまり中間体のスーパーオキシド
(O2 -)、ペルオキシド(O2 2-)、及びヒドロキシラ
ジカル(OH-)は毒性があり、特にOHやO2 -の酸化
能力は強く、生体内ではO2 -はSODによって、過酸化
水素に還元され、更に過酸化水素はカタラーゼ(過酸化
水素を水と酸素に分解するための触媒の働きをするヘム
タンパク質酵素)によって水と酸素に分解される。しか
し、通性嫌気性細菌や絶対嫌気性細菌の中の大半はカタ
ラーゼを持たないので、中間体の毒性を無毒化すること
ができない。したがって、一般細菌に対しては、水の酸
化還元電位の低減によって気体中の酸素の溶解度を高
め、酸素分子が還元されて水分子を生成するまでに発生
する中間体の毒性により、殺菌作用を及ぼすことができ
る。
That is, the intermediates superoxide (O 2 ), peroxide (O 2 2− ), and hydroxyl radical (OH ) are toxic, and the oxidizing ability of OH and O 2 is particularly strong. O 2 - is reduced to hydrogen peroxide by SOD, and hydrogen peroxide is further decomposed into water and oxygen by catalase (a heme protein enzyme that acts as a catalyst for decomposing hydrogen peroxide into water and oxygen). . However, most of the facultative anaerobic bacteria and obligate anaerobic bacteria do not have catalase, so that the toxicity of the intermediate cannot be detoxified. Therefore, against general bacteria, the solubility of oxygen in the gas is increased by reducing the oxidation-reduction potential of water, and the toxic effect of intermediates generated before oxygen molecules are reduced to produce water molecules has a bactericidal effect. Can exert.

【0016】次に、悪臭物質の除去に適用した例を説明
する。臭気の発生は、以下の悪臭物質が特に発生した場
合不快感を及ぼすことになる。塩基性系統では、アンモ
ニア、トリメチルアミン等であり、酸性系統では、硫化
水素、メチルメルカプタンであり、中性系統では、二硫
化ジメチル、硫化ジメチル、アセトアルデヒドである。
Next, an example in which the present invention is applied to the removal of malodorous substances will be described. Odor generation may cause discomfort when the following malodorous substances are generated in particular. In the basic system, ammonia and trimethylamine are used. In the acidic system, hydrogen sulfide and methyl mercaptan are used. In the neutral system, dimethyl disulfide, dimethyl sulfide, and acetaldehyde are used.

【0017】アンモニアNH3は、酸化還元電位の低下
によってシステム内の水が自由電子によって解離し易く
なり、この水に溶解して脱臭される。硫化水素H2
は、還元水によって容解が促進されて遊離硫黄が沈澱す
る。
Ammonia NH 3 is easily dissociated by free electrons due to the reduction of the oxidation-reduction potential due to free electrons, and is dissolved in the water to be deodorized. Hydrogen sulfide H 2 S
Is dissolved by reduced water, and free sulfur is precipitated.

【0018】[0018]

【発明の効果】以上述べたように、本発明によれば、焼
却灰を1200〜1300℃の温度において2回の焼成
を行なうことにより、焼却灰を溶融してガラス化し、ガ
ラス状分子構造の中に有害物質や重金属を取り込むこと
ができ、焼却灰が水浄化材の陶器基材の原料をなす有価
資源となる。
As described above, according to the present invention, by burning the incinerated ash twice at a temperature of 1200 to 1300 ° C., the incinerated ash is melted and vitrified to have a glassy molecular structure. Hazardous substances and heavy metals can be taken in, and the incinerated ash is a valuable resource that is used as a raw material of the pottery base material for water purification materials.

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

【図1】本発明の実施の形態における水浄化材を示す模
式図である。
FIG. 1 is a schematic diagram showing a water purification material according to an embodiment of the present invention.

【図2】同水浄化材の実験における使用状態を示す説明
図である。
FIG. 2 is an explanatory diagram showing a use state of the water purification material in an experiment.

【符号の説明】[Explanation of symbols]

1 水浄化材 2 陶器基材 3 釉薬部 4 ケーシング Reference Signs List 1 water purifying material 2 pottery base material 3 glaze part 4 casing

─────────────────────────────────────────────────────
────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成11年2月5日[Submission date] February 5, 1999

【手続補正1】[Procedure amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】請求項1[Correction target item name] Claim 1

【補正方法】変更[Correction method] Change

【補正内容】[Correction contents]

【手続補正2】[Procedure amendment 2]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0005[Correction target item name] 0005

【補正方法】変更[Correction method] Change

【補正内容】[Correction contents]

【0005】[0005]

【課題を解決するための手段】上記した課題を解決する
ために、本発明の焼却灰を有価資源化した水浄化材の製
造方法は、都市ごみ焼却灰と窯業原料用鉱物粘土とを適
当比の割合で混合して後に適当形状に造型し、この造型
物を適当温度で溶融焼成して陶器基材を形成し、陶器基
材に釉薬を塗布して再び適当温度で焼成するものであっ
て、釉薬が、水の分子振動スペクトルの内で、赤外線の
波長領域において最大の分子振動スペクトルを発する伸
縮振動または変角振動を持ち、その結晶において励起す
る内部振動の振動エネルギーを水分子に伝達して電子を
励起し、水和電子を派生させる鉱物の粉体を含む構成と
したものである。
Means for Solving the Problems In order to solve the above-mentioned problems, a method for producing a water purifying material using incinerated ash as a valuable resource according to the present invention comprises an appropriate ratio of municipal waste incinerated ash to mineral clay for ceramic raw materials. And then molded into an appropriate shape, melt molded and fired at an appropriate temperature to form a ceramic substrate, apply a glaze to the ceramic substrate, and fire again at an appropriate temperature. , glaze, among the molecular vibrational spectra of water, Chi lifting a stretching vibration or deformation vibration emits the greatest molecular vibrational spectra in a wavelength region of infrared, to excite the crystal
Transfer the vibration energy of internal vibration to water molecules to generate electrons
It is configured to include a mineral powder that excites and generates hydrated electrons .

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI C04B 35/00 V ──────────────────────────────────────────────────の Continued on front page (51) Int.Cl. 6 Identification code FI C04B 35/00 V

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 都市ごみ焼却灰と窯業原料用鉱物粘土と
を適当比の割合で混合して後に適当形状に造型し、この
造型物を適当温度で溶融焼成して陶器基材を形成し、陶
器基材に釉薬を塗布して再び適当温度で焼成するもので
あって、 釉薬が、水の分子振動スペクトルの内で、赤外線の波長
領域において最大の分子振動スペクトルを発する伸縮振
動または変角振動を持つ鉱物の粉体を含むことを特徴と
する焼却灰を有価資源化した水浄化材の製造方法。
Claims 1. An incinerated ash from municipal solid waste and a mineral clay for a ceramic raw material are mixed at an appropriate ratio and then molded into an appropriate shape, and the molded product is melted and fired at an appropriate temperature to form a ceramic base material. A glaze is applied to a ceramic substrate and fired again at an appropriate temperature. The glaze is a stretching vibration or a bending vibration that emits the largest molecular vibration spectrum in the infrared wavelength region of the molecular vibration spectrum of water. A method for producing a water purification material using incinerated ash as a valuable resource, characterized by containing a mineral powder having the following.
JP10009181A 1997-06-20 1998-01-21 Production of water clarifying material by recycling incineration ash as valuable resource Pending JPH11209189A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP10009181A JPH11209189A (en) 1998-01-21 1998-01-21 Production of water clarifying material by recycling incineration ash as valuable resource
TW87120112A TW434200B (en) 1997-06-20 1998-12-03 Reforming material for fluid material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10009181A JPH11209189A (en) 1998-01-21 1998-01-21 Production of water clarifying material by recycling incineration ash as valuable resource

Publications (1)

Publication Number Publication Date
JPH11209189A true JPH11209189A (en) 1999-08-03

Family

ID=11713395

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10009181A Pending JPH11209189A (en) 1997-06-20 1998-01-21 Production of water clarifying material by recycling incineration ash as valuable resource

Country Status (1)

Country Link
JP (1) JPH11209189A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2799664A1 (en) * 1999-10-14 2001-04-20 Raymond Gleizes Treatment of liquid, semi-liquid or solid media containing pollutants comprises using a particulate material comprising household waste incineration residue containing at least 20 wt.% calcium
JP2007105677A (en) * 2005-10-14 2007-04-26 Mikasa:Kk Active water production method, animal breeding method, and active water
JP2010275343A (en) * 2009-05-26 2010-12-09 Kanto Kanzai:Kk Filter medium for soil improvement, method for manufacturing the filter medium for soil improvement, and method of soil improvement using the filter medium for soil improvement
CN102133576A (en) * 2010-01-22 2011-07-27 株式会社关东管财 Eco-resource slag effective utilization system

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2799664A1 (en) * 1999-10-14 2001-04-20 Raymond Gleizes Treatment of liquid, semi-liquid or solid media containing pollutants comprises using a particulate material comprising household waste incineration residue containing at least 20 wt.% calcium
JP2007105677A (en) * 2005-10-14 2007-04-26 Mikasa:Kk Active water production method, animal breeding method, and active water
JP2010275343A (en) * 2009-05-26 2010-12-09 Kanto Kanzai:Kk Filter medium for soil improvement, method for manufacturing the filter medium for soil improvement, and method of soil improvement using the filter medium for soil improvement
CN102133576A (en) * 2010-01-22 2011-07-27 株式会社关东管财 Eco-resource slag effective utilization system
CN102133576B (en) * 2010-01-22 2016-01-06 株式会社关东管财 The effective Application way of eco-resource slag

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