JPH10212154A - Production of glassy fired body, using incineration ash of industrial waste and general waste as raw material - Google Patents
Production of glassy fired body, using incineration ash of industrial waste and general waste as raw materialInfo
- Publication number
- JPH10212154A JPH10212154A JP9011765A JP1176597A JPH10212154A JP H10212154 A JPH10212154 A JP H10212154A JP 9011765 A JP9011765 A JP 9011765A JP 1176597 A JP1176597 A JP 1176597A JP H10212154 A JPH10212154 A JP H10212154A
- Authority
- JP
- Japan
- Prior art keywords
- waste
- industrial waste
- incinerated ash
- glassy
- general
- 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
Links
Landscapes
- Compositions Of Oxide Ceramics (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】この発明は、産業廃棄物並び
に一般廃棄物の焼却灰を原料とするガラス状焼成物の製
造方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for producing a glassy fired product from incinerated ash of industrial waste and general waste.
【0002】[0002]
【従来の技術】従来、産業廃棄物や一般廃棄物は、以下
の3通りの方法にて処理されている。2. Description of the Related Art Conventionally, industrial waste and general waste are treated by the following three methods.
【0003】産業廃棄物や一般廃棄物を、600〜8
50℃程度の温度で焼却し、その焼却灰を最終処分場に
投棄して処理する方法。[0003] Industrial waste and general waste are reduced to 600 to 8
A method in which incineration is performed at a temperature of about 50 ° C, and the incinerated ash is discarded at a final disposal site for treatment.
【0004】産業廃棄物や一般廃棄物を、600〜8
50℃程度の温度で焼却し、その焼却灰にセメント等の
硬化材と水と骨材を加えて固化形成し、ブロック等の二
次製品とする方法。[0004] Industrial waste and general waste are reduced to 600 to 8
A method of incineration at a temperature of about 50 ° C., and adding a hardening material such as cement, water and aggregate to the incinerated ash to form a solid product, thereby obtaining a secondary product such as a block.
【0005】産業廃棄物や一般廃棄物を、600〜8
50℃程度の温度で焼却し、その焼却灰をさらに高温の
1300〜1800℃程度の温度で溶融スラグ化する方
法。なお、かかる溶融スラグは、セメントコンクリート
用骨材や、粉砕・成形後再焼成したインターブロッキン
グ材として、あるいは陶磁器用のガラス成分として陶磁
器用粘土に加えるなどして利用される。[0005] Industrial waste and general waste are reduced to 600 to 8
A method in which incineration is performed at a temperature of about 50 ° C., and the incinerated ash is further melted at a high temperature of about 1300 to 1800 ° C. The molten slag is used as an aggregate for cement concrete, an interblocking material which has been pulverized, molded and refired, or added to a clay for ceramics as a glass component for ceramics.
【0006】[0006]
【発明が解決しようとする課題】ところが、上記した従
来の方法では、未だ下記の問題点が残されていた。However, the conventional method described above still has the following problems.
【0007】すなわち、の方法では、焼却灰に含まれ
る重金属やハロゲン化有機物等が金属、酸化物及び塩化
物等の状態で残存しているため、長期にわたる雨水や地
下水等の影響を受けて重金属やハロゲン化有機物が水の
中に溶出する。That is, in the method (1), heavy metals and halogenated organic substances contained in the incineration ash remain in the form of metals, oxides and chlorides, and are thus affected by rainwater and groundwater for a long period of time. And halogenated organics elute in water.
【0008】このような重金属やハロゲン化有機物の溶
出は、自然界の動植物に多大な影響を与えるとともに、
人体にも悪影響を及ぼす環境破壊を引き起こすことにな
り、大きな社会問題となるおそれがある。[0008] Such elution of heavy metals and halogenated organic substances has a great effect on animals and plants in the natural world,
This can cause environmental destruction that has an adverse effect on the human body, and can be a major social problem.
【0009】しかも、近年の大量消費型の生活様式の広
がりにより、ごみの排出量は年々増加する傾向にあり、
かかる状況下において、各自治体が所有する最終処分場
の許容年数は約8年といわれている。他方、地方自治体
での新たな最終処分場の建設は、処分場用地の選定・取
得及び地域への補償問題等を抱え、遅々として進まない
という状況となっている。Furthermore, with the spread of the mass-consumption type of lifestyle in recent years, the amount of garbage discharged tends to increase year by year.
Under such circumstances, it is said that the permissible life of the final disposal site owned by each municipality is about eight years. On the other hand, the construction of a new landfill site by local governments has been slow, with problems such as the selection and acquisition of landfill sites and compensation for the area.
【0010】の方法では、と同様に、焼却灰に含ま
れる重金属やハロゲン化有機物等が金属、酸化物及び塩
化物の状態でセメントコンクリート中に残存しているた
め、雨水や地下水によるセメントコンクリートの吸水・
透水現象で重金属やハロゲン化有機物等がセメントコン
クリート外に溶出してやはり環境破壊を引き起こすおそ
れがある。In the method of (1), heavy metals and halogenated organic substances contained in the incineration ash remain in the cement concrete in the form of metals, oxides and chlorides in the same manner as in the above method. Water absorption
Due to the water permeation phenomenon, heavy metals, halogenated organic substances, and the like may elute out of the cement concrete, which may also cause environmental destruction.
【0011】また、の方法では、焼却灰に含まれる重
金属やハロゲン化有機物等は珪酸を主成分とするスラグ
相に固溶しているため、雨水や地下水等の影響を受けて
重金属やハロゲン化有機物等が水中に溶出することはな
い。しかし、焼却灰を再焼成して溶融スラグを製造する
装置は焼却灰1トン当たり約1億円程度と高価であり、
また、ランニングコストも焼却灰1トン当たり1万円程
度かかることから、財政事情の苦しい地方自治体では処
理装置を建設することが難しい。In the method (1), since heavy metals and halogenated organic substances contained in the incinerated ash are dissolved in a slag phase mainly composed of silicic acid, heavy metals and halogenated organic substances are affected by rainwater and groundwater. Organic substances do not elute in water. However, the equipment for re-firing incinerated ash to produce molten slag is expensive at about 100 million yen per ton of incinerated ash,
In addition, the running cost is about 10,000 yen per ton of incinerated ash, so it is difficult for local governments with difficult financial conditions to construct a processing apparatus.
【0012】[0012]
【課題を解決するための手段】本発明は、上記課題を解
決することのできる産業廃棄物並びに一般廃棄物の焼却
灰を原料とするガラス状焼成物の製造方法を提供するこ
とを目的とし、産業廃棄物もしくは一般廃棄物の少なく
ともいずれかの焼却灰と陶磁器用粘土との混合物や、産
業廃棄物もしくは一般廃棄物の少なくともいずれかの焼
却灰、あるいはこれに火山性堆積物を混合した混合物に
水と骨材と硬化材とを混合したスラリーを固化成形した
成形物を焼成・ガラス化してガラス状焼成物を得ること
とした。SUMMARY OF THE INVENTION It is an object of the present invention to provide a method for producing a glassy fired product from incinerated ash of industrial waste and general waste, which can solve the above-mentioned problems. For a mixture of incinerated ash of at least one of industrial waste and general waste and clay for ceramics, or an incinerated ash of at least one of industrial waste and general waste, or a mixture of the same and volcanic sediment A molded product obtained by solidifying and molding a slurry in which water, an aggregate, and a hardening material were mixed was fired and vitrified to obtain a glass-like fired material.
【0013】かかる方法により得られるガラス状焼成物
は、重金属やハロゲン化有機物が溶出することなく安全
であり、しかも、これを製造するための設備投資やラン
ニングコストが安価となる。[0013] The glassy fired product obtained by such a method is safe without heavy metals and halogenated organic substances being eluted, and the equipment investment and running costs for producing the same are low.
【0014】[0014]
【発明の実施の形態】本発明は、産業廃棄物もしくは一
般廃棄物の少なくともいずれかの焼却灰を再焼成してガ
ラス化するものである。BEST MODE FOR CARRYING OUT THE INVENTION The present invention is to vitrify at least one of industrial waste and general waste by recalcining.
【0015】再焼成するに際しては、前記焼却灰に陶磁
器用粘土を混合するか、または、前記焼却灰、あるいは
これに火山性堆積物を混合した混合物に水と骨材と硬化
材とを混合したスラリーを固化成形した成形物を焼成す
ることが好ましい。In re-firing, water, aggregate and hardening material are mixed with the incinerated ash or a mixture of the incinerated ash and the volcanic sediment. It is preferable to fire a molded product obtained by solidifying and forming the slurry.
【0016】このように、本発明は、有害物質を溶出し
ないようにするとともに、直接製品の形にできるという
特徴を有する。As described above, the present invention is characterized in that harmful substances are prevented from being eluted and that it can be directly formed into a product.
【0017】また、使用する装置も既存の窯や設備を利
用することができるために処理コストがかからないとい
う特徴を有する。Further, since the apparatus to be used can use existing kilns and equipment, there is a feature that no processing cost is required.
【0018】さらに、焼却灰中に含まれる重金属やハロ
ゲン化有機物を焼成物中に封入することができるので、
雨水や地下水などにより外部に溶出することがなく、こ
れを埋め立てに利用しても環境破壊を引き起こすおそれ
がなく、また、これを最終処理場で処分する場合でも、
最終処理場に莫大な環境破壊対策費用を投じる必要がな
いので産業廃棄物や一般廃棄物の処理コストを大きく低
減することができ、処理業者や地方自治体の経費削減に
大きく寄与する。Furthermore, since heavy metals and halogenated organic substances contained in the incineration ash can be encapsulated in the fired material,
It does not elute to the outside due to rainwater or groundwater, and there is no risk of causing environmental destruction even if it is used for landfill, and even if this is disposed of at the final treatment plant,
Since there is no need to invest huge costs for environmental destruction at the final disposal site, the cost of treating industrial waste and general waste can be greatly reduced, greatly contributing to cost reductions for disposal companies and local governments.
【0019】しかも、ガラス状焼成物は、透水性タイ
ル、植木鉢、瓦、花壇用ブロック、敷設用ブロック、漁
礁用ブロック等の二次製品として有効利用することがで
きるため、新たな市場開拓が可能であり、経済浮揚の効
果が大きい。Moreover, the glassy fired product can be effectively used as a secondary product such as a permeable tile, a flowerpot, a tile, a flowerbed block, a laying block, a fishing reef block, and thus a new market can be developed. The effect of economic levitation is great.
【0020】また、透水性や軽量という特性を有するの
で、機能性分野での利用も可能である。Further, since it has characteristics such as water permeability and light weight, it can be used in the field of functionality.
【0021】ところで、焼却灰と陶磁器用粘土とは、重
量比で1:1の割合とし、さらに、自然乾燥、もしくは
硬化材の添加により硬化させて1200〜1300℃の
温度で焼成する。By the way, the incinerated ash and the clay for porcelain are in a ratio of 1: 1 by weight, and are further cured by natural drying or addition of a curing agent and fired at a temperature of 1200 to 1300 ° C.
【0022】また、前記骨材としては石英を、硬化材と
してはアルミナセメントを好適に用いることができ、所
望する形状の型内で自然硬化させた後に所定時間(例え
ば24時間)乾燥させ、次いで、1230〜1260℃
の温度で焼成するとよい。Quartz can be suitably used as the aggregate, and alumina cement can be suitably used as the hardening material. The material is naturally hardened in a mold having a desired shape, dried for a predetermined time (for example, 24 hours), and then dried. , 1230-1260 ° C
It is good to bake at the temperature.
【0023】さらに、前記ガラス状焼成物に、釉薬を塗
布して再焼成すると、陶器の代用品として利用すること
が可能となる。Further, when the glassy fired product is coated with glaze and refired, it can be used as a substitute for pottery.
【0024】なお、上記焼却灰は、産業廃棄物並びに一
般廃棄物の各単体を焼却したものでも、あるいは、両者
を混合したものでも構わない。The incinerated ash may be incinerated industrial waste and general waste, or may be a mixture of both.
【0025】[0025]
【実施例】以下、本発明の実施例を具体的に説明する。DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the present invention will be specifically described below.
【0026】(実施例1)産業廃棄物や一般廃棄物、あ
るいは両者が混合した廃棄物を約600〜850℃の温
度で焼却した後の焼却灰を原料とし、これと陶磁器用粘
土とを1:1の割合で混合した後、この混合物を乾燥・
硬化させるか、あるいは、ポリアクリル酸系エマルジョ
ン等の硬化材を添加して硬化させたものを、窯内におい
て1200〜1300℃の温度で焼成した。硬化物は焼
成により溶融し、褐色のガラス状発泡体となった。(Example 1) An incinerated ash obtained by incinerating industrial waste, general waste or a mixed waste thereof at a temperature of about 600 to 850 ° C is used as a raw material. After mixing at a ratio of 1: 1, the mixture is dried.
What was cured or cured by adding a curing agent such as a polyacrylic acid emulsion was fired in a kiln at a temperature of 1200 to 1300 ° C. The cured product was melted by firing to form a brown glassy foam.
【0027】(実施例2)産業廃棄物や一般廃棄物、あ
るいは両者が混合した廃棄物を約600〜850℃の温
度で焼却した後の焼却灰を原料とし、これに、骨材とし
ての粗粒石英又は微粒石英と、硬化材としてのアルミナ
セメントと、水とを混合してスラリーを得た。(Example 2) An incinerated ash obtained by incinerating industrial waste, general waste, or a waste in which both are mixed at a temperature of about 600 to 850 ° C is used as a raw material. A slurry was obtained by mixing grained or fine quartz, alumina cement as a hardening material, and water.
【0028】混合割合は、重量比で以下の4通りとし
た。The mixing ratio was the following four types by weight.
【0029】焼却灰:粗粒石英:アルミナセメント:
水=50:50:30:50 焼却灰:粗粒石英:アルミナセメント:水=60:4
0:30:50 焼却灰:微粒石英:アルミナセメント:水=50:5
0:30:50 焼却灰:微粒石英:アルミナセメント:水=60:4
0:30:50 上記各スラリーを所定の型枠内に投入し、それぞれ、2
5℃で24時間放置して自然硬化させた後、型枠から外
してさらに25℃で72時間硬化させた。Incinerated ash: coarse quartz: alumina cement:
Water = 50: 50: 30: 50 Incinerated ash: coarse quartz: alumina cement: water = 60: 4
0:30:50 Incinerated ash: fine quartz: alumina cement: water = 50: 5
0:30:50 Incinerated ash: fine quartz: alumina cement: water = 60: 4
0:30:50 Each of the above slurries was charged into a predetermined mold,
After leaving it to stand at 5 ° C. for 24 hours to cure it naturally, it was removed from the mold and further cured at 25 ° C. for 72 hours.
【0030】硬化物は、105℃の乾燥器で一昼夜乾燥
させた後、900〜1260℃の温度範囲で焼成した。The cured product was dried in a dryer at 105 ° C. for a whole day and night, and then fired in a temperature range of 900 to 1260 ° C.
【0031】いずれの焼成物も、1150℃以下では焼
却灰がガラス化しないため、形状を保持できなかった
が、1150〜1200℃では砂岩のような硬さを有す
る焼結体となり、1200〜1260℃では多少の取り
扱いでは壊れることのない頑強な硬さを有するガラス状
焼成物が得られた。In any of the calcined products, the incinerated ash was not vitrified at 1150 ° C. or lower, so that the shape could not be maintained. However, at 1150 to 1200 ° C., the sintered body had a hardness like sandstone and was 1200 to 1260. At ℃, a glassy fired product having robust hardness which was not broken by some handling was obtained.
【0032】これを窯内で900〜1200℃の範囲で
段階的に焼成した。This was fired stepwise in a kiln at 900 to 1200 ° C.
【0033】(実施例3)産業廃棄物や一般廃棄物、あ
るいは両者が混合した廃棄物を約600〜850℃の温
度で焼却した後の焼却灰を原料とし、これに火山性堆積
物として火山灰を混合し、さらに、骨材としての微粒石
英と、硬化材としてのアルミナセメントと、水とを混合
してスラリーを得た。(Example 3) As a raw material, incinerated ash obtained by incinerating industrial waste, general waste, or a mixed waste of both at a temperature of about 600 to 850 ° C is used as a raw material. Were mixed, and further, fine quartz as an aggregate, alumina cement as a hardening material, and water were mixed to obtain a slurry.
【0034】混合割合は、重量比で以下の2通りとし
た。The mixing ratio was the following two types by weight.
【0035】焼却灰:火山灰:微粒石英:アルミナセ
メント:水=45:15:40:30:50 焼却灰:火山灰:微粒石英:アルミナセメント:水=
30:30:40:30:50 上記各スラリーを板状の型枠内に鋳込み、それぞれ、2
5℃で24時間放置して自然硬化させた後、型枠から外
してさらに25℃で72時間硬化させた。Incinerated ash: volcanic ash: fine quartz: alumina cement: water = 45: 15: 40: 30: 50 Incinerated ash: volcanic ash: fine quartz: alumina cement: water =
30: 30: 40: 30: 50 Each of the above slurries was cast into a plate-shaped mold,
After leaving it to stand at 5 ° C. for 24 hours to cure it naturally, it was removed from the mold and further cured at 25 ° C. for 72 hours.
【0036】硬化物は、105℃の乾燥器で一昼夜乾燥
させた後、1200〜1260℃の温度範囲で焼成し
た。The cured product was dried all day and night in a dryer at 105 ° C., and then fired in a temperature range of 1200 to 1260 ° C.
【0037】いずれの焼成物も、しっかりと焼き固まっ
たタイル状になっており、上面から水をかけると吸水
し、さらに水を増加すると下面から滴り落ちる程の透水
性を有するガラス状焼成物が得られた。Each of the fired products has a tile shape which is firmly baked and solidified. When water is applied from the upper surface, water is absorbed, and when the amount of water is further increased, a glass-like fired material having water permeability enough to drip from the lower surface is obtained. Obtained.
【0038】(実施例4)先の実施例3で得たガラス状
焼成物に釉薬を塗布し、1250℃の温度で再焼成する
と、表面に光沢のあるガラス状焼成物が得られた。これ
は、内部はポーラスで軽量であるが、釉薬層がしっかり
と形成されているため水を通さない性質を有することが
分かった。Example 4 A glaze was applied to the glassy fired product obtained in Example 3 and refired at a temperature of 1250 ° C., whereby a glassy fired product having a glossy surface was obtained. This was found to be porous and lightweight inside, but had the property of being impermeable to water because the glaze layer was firmly formed.
【0039】以上の各実施例で得られたガラス状生成物
は、焼却灰中に含まれる重金属やハロゲン化有機物をガ
ラス質中に封入することができ、雨水や地下水などによ
り外部に溶出することがないのでこれを埋め立てても環
境破壊を引き起こすおそれがなく、また、かかるガラス
状焼成物を、例えば、透水性タイルなどの機能製品とな
すことができ、また、軽くて扱いやすく安全なので植木
ばちや瓦、あるいは、花壇用ブロックや敷設用ブロッ
ク、魚礁用ブロックなどの製品として、さらには、土木
用栗石などにも有効利用することができる。The glassy product obtained in each of the above examples can encapsulate heavy metals and halogenated organic substances contained in incineration ash into glass, and can be eluted outside by rainwater or groundwater. There is no risk of causing environmental destruction even if it is landfilled.In addition, such a glassy fired material can be used as a functional product such as a permeable tile. It can be effectively used as products such as chicks and tiles, blocks for flower beds, blocks for laying, blocks for fish reefs, and also, for example, chestnuts for civil engineering.
【0040】また、実施例4で示したように、ガラス状
焼成物に釉薬を施したものは、陶器の代用品としても利
用可能である。Further, as shown in Example 4, a glass-like fired product provided with a glaze can be used as a substitute for pottery.
【0041】[0041]
【発明の効果】本発明は、上記した形態で実施されるも
ので以下の効果を奏する。The present invention is embodied in the above-described embodiment and has the following effects.
【0042】請求項1記載の本発明では、産業廃棄物
もしくは一般廃棄物の少なくともいずれかの焼却灰と陶
磁器用粘土とを混合し、同混合物を焼成して産業廃棄物
並びに一般廃棄物の焼却灰を原料とするガラス状焼成物
を得ている。したがって、焼却灰中に含まれる重金属や
ハロゲン化有機物をガラス質中に封入することができ、
容易かつ安全に処分することができるとともに、これを
二次製品として利用することができ、新たな市場開拓が
可能となって、経済の浮揚効果が大きい。According to the present invention, incineration ash of at least one of industrial waste and general waste is mixed with clay for ceramics, and the mixture is fired to incinerate industrial waste and general waste. A glassy fired product using ash as a raw material has been obtained. Therefore, heavy metals and halogenated organic substances contained in the incineration ash can be encapsulated in the vitreous material,
It can be disposed of easily and safely, and can be used as a secondary product, enabling the development of a new market and a great economic levitation effect.
【0043】請求項2記載の本発明では、産業廃棄物
もしくは一般廃棄物の少なくともいずれかの焼却灰に水
と骨材と硬化材とを混合して得たスラリーを、型内に投
入して固化成形し、その後、成形物を焼成して産業廃棄
物並びに一般廃棄物の焼却灰を原料とするガラス状焼成
物を得ている。したがって、焼却灰中に含まれる重金属
やハロゲン化有機物をガラス質中に封入することがで
き、容易かつ安全に処分することができるとともに、こ
れを所望形状の二次製品として利用することができ、新
たな市場開拓が可能となって、経済の浮揚効果が大き
い。According to the second aspect of the present invention, a slurry obtained by mixing water, aggregate and hardened material into incinerated ash of at least one of industrial waste and general waste is put into a mold. Solidification molding is performed, and then the molded product is fired to obtain a glassy fired product made from incinerated ash of industrial waste and general waste. Therefore, heavy metals and halogenated organic substances contained in the incineration ash can be encapsulated in the vitreous material, and can be easily and safely disposed, and can be used as a secondary product having a desired shape. New market development is possible, and the economic levitation effect is great.
【0044】請求項3記載の本発明では、産業廃棄物
もしくは一般廃棄物の少なくともいずれかの焼却灰に火
山性堆積物を混合し、同混合物に水と骨材と硬化材とを
混合して得たスラリーを、型内に投入して固化成形し、
その後、成形物を焼成して産業廃棄物並びに一般廃棄物
の焼却灰を原料とするガラス状焼成物を得ている。した
がって、これを透水性タイルなどの機能製品として再利
用することができるとともに、軽くて扱いやすく安全な
ので植木ばちや瓦、あるいは、花壇用ブロックや敷設用
ブロック、魚礁用ブロックなどに、さらには、土木用栗
石などにも有効利用することができ、新たな市場開拓が
可能となって、経済の浮揚効果が大きい。According to the third aspect of the present invention, at least one of the incineration ash of industrial waste and general waste is mixed with volcanic sediment, and the mixture is mixed with water, aggregate and hardened material. The obtained slurry is put into a mold and solidified and molded,
After that, the molded product is fired to obtain a glassy fired product made from incinerated ash of industrial waste and general waste. Therefore, this can be reused as a functional product such as a permeable tile, and it is light, easy to handle and safe, so it can be used for planting bees and tiles, or flowerbed blocks, laying blocks, fish reef blocks, and more. It can also be used effectively for rubble stones for civil engineering, etc., enabling the development of new markets and a great economic levitation effect.
【0045】請求項4記載の本発明では、成形物を一
度焼成した後のガラス状焼成物に、釉薬を施して再焼成
して産業廃棄物並びに一般廃棄物の焼却灰を原料とする
ガラス状焼成物を得ている。したがって、内部はポーラ
スでありながら、表面に光沢を有し、かつ、水を通さな
い性質を有するため、軽量な陶磁器代用品として利用す
ることができる。According to the fourth aspect of the present invention, the glassy fired material obtained by firing the molded product once is subjected to glaze and refired to produce a glassy material obtained from incinerated ash of industrial waste and general waste. A fired product has been obtained. Therefore, although the inside is porous, it has a glossy surface and has the property of impervious to water, so that it can be used as a lightweight ceramic substitute.
Claims (4)
ともいずれかの焼却灰と陶磁器用粘土とを混合し、同混
合物を焼成して得ることを特徴とする産業廃棄物並びに
一般廃棄物の焼却灰を原料とするガラス状焼成物の製造
方法。An incinerated ash for industrial waste and general waste, characterized by mixing incinerated ash of at least one of industrial waste and general waste with clay for porcelain and firing the mixture. A method for producing a glassy fired product using as a raw material.
ともいずれかの焼却灰に水と骨材と硬化材とを混合して
得たスラリーを、型内に投入して固化成形し、その後、
成形物を焼成して得ることを特徴とする産業廃棄物並び
に一般廃棄物の焼却灰を原料とするガラス状焼成物の製
造方法。2. A slurry obtained by mixing water, aggregate, and hardening material with at least one of incineration ash of industrial waste or general waste is poured into a mold and solidified and formed.
A method for producing a glass-like fired product from incinerated ash of industrial waste and general waste, which is obtained by firing a molded product.
ともいずれかの焼却灰に火山性堆積物を混合し、同混合
物に水と骨材と硬化材とを混合して得たスラリーを、型
内に投入して固化成形し、その後、成形物を焼成して得
ることを特徴とする産業廃棄物並びに一般廃棄物の焼却
灰を原料とするガラス状焼成物の製造方法。3. A slurry obtained by mixing volcanic sediment with incinerated ash of at least one of industrial waste and general waste, and mixing the mixture with water, aggregate and hardened material. A method for producing a glass-like fired material using incinerated ash of industrial waste and general waste as a raw material, wherein the material is obtained by solidifying and then firing the molded product.
状焼成物に、釉薬を施した後に再焼成して得ることを特
徴とする産業廃棄物並びに一般廃棄物の焼却灰を原料と
するガラス状焼成物の製造方法。4. The incinerated ash of industrial waste and general waste, obtained by applying a glaze to the glassy fired product according to any one of claims 1 to 3 and then refiring it. For producing a vitreous fired product.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP01176597A JP3535334B2 (en) | 1997-01-24 | 1997-01-24 | Method for producing burned material from incinerated ash of industrial waste and general waste |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP01176597A JP3535334B2 (en) | 1997-01-24 | 1997-01-24 | Method for producing burned material from incinerated ash of industrial waste and general waste |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH10212154A true JPH10212154A (en) | 1998-08-11 |
JP3535334B2 JP3535334B2 (en) | 2004-06-07 |
Family
ID=11787083
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP01176597A Expired - Lifetime JP3535334B2 (en) | 1997-01-24 | 1997-01-24 | Method for producing burned material from incinerated ash of industrial waste and general waste |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3535334B2 (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20020067785A (en) * | 2001-02-19 | 2002-08-24 | 지경섭 | manufacture method of infra-red rays emission bricks |
JP2007029933A (en) * | 2005-07-29 | 2007-02-08 | Tokyo Kiyuuei:Kk | Sediment improving material and sediment improving method |
CN102924090A (en) * | 2012-11-02 | 2013-02-13 | 鹰牌陶瓷实业(河源)有限公司 | Vitrified ceramic tile blank and vitrified ceramic tile preparation method thereof |
-
1997
- 1997-01-24 JP JP01176597A patent/JP3535334B2/en not_active Expired - Lifetime
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20020067785A (en) * | 2001-02-19 | 2002-08-24 | 지경섭 | manufacture method of infra-red rays emission bricks |
JP2007029933A (en) * | 2005-07-29 | 2007-02-08 | Tokyo Kiyuuei:Kk | Sediment improving material and sediment improving method |
CN102924090A (en) * | 2012-11-02 | 2013-02-13 | 鹰牌陶瓷实业(河源)有限公司 | Vitrified ceramic tile blank and vitrified ceramic tile preparation method thereof |
Also Published As
Publication number | Publication date |
---|---|
JP3535334B2 (en) | 2004-06-07 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Ramadan et al. | Reuse of water treatment plant sludge in brick manufacturing | |
JP5658270B2 (en) | Manufacturing method of lightweight construction materials using sludge waste | |
CN106810137A (en) | Purification type water-permeable brick and its manufacture method | |
JP3188200B2 (en) | Manufacturing method of artificial lightweight aggregate | |
JPS62212260A (en) | Method of converting waste matter to ceramics | |
JP3535334B2 (en) | Method for producing burned material from incinerated ash of industrial waste and general waste | |
KR100971283B1 (en) | Stroll path and bicycleexclusive road pavement using natural materials | |
KR20040080631A (en) | a | |
KR100450898B1 (en) | production of incinerated construction materials using wastewater sludge | |
KR20120008557A (en) | Method for manufacturing standardization product by using sludge | |
KR101022895B1 (en) | Protective block for roadside tree and manufacture method thereof | |
KR100370268B1 (en) | The method of construction materials composition use for refuse lime | |
JPH10204432A (en) | Material for stabilizing soil | |
JP2001353479A (en) | Sintered body by safening reaction of building waste material containing asbestos | |
CN110436886A (en) | A kind of method that the cyclic utilization of waste prepares haydite | |
CN114656182B (en) | Artificial pebble ceramsite | |
EP0466877B1 (en) | Process for environmentally safe disposal of noxious solid, liquidand/or gaseous substances at temperatures of 400 to 1800 degrees celsius | |
JP2000319048A (en) | Concrete product using hydraulic calcined product as binding material | |
JPH06144898A (en) | Mixed hydraulic substance, hardened material and burnt material | |
JP4155773B2 (en) | Cured body | |
RU2692340C1 (en) | Method of erecting an ellipsoidal enclosure wall (embankment) on landfill of ash utilization from combustion of sewage sludge | |
TWI440610B (en) | Method for generating sludge sludge | |
JP2004161609A (en) | Firing and sintering method for incineration ash or for lightweight fine-grained material using the incineration ash as raw material, and sintered product obtained by the method | |
JPH1059765A (en) | Production of ceramic raw material and manufacture of ceramic tile by effectively utilizing molten slag of waste incineration ash | |
KR20010092829A (en) | Stabilization Method of Heavy Metal in Fly Ash and Aggregate Produced Thereby |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 20020212 |
|
A521 | Written amendment |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20040107 |
|
A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20040311 |
|
R150 | Certificate of patent or registration of utility model |
Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20090319 Year of fee payment: 5 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20100319 Year of fee payment: 6 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20110319 Year of fee payment: 7 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20130319 Year of fee payment: 9 |