JP3535334B2 - Method for producing burned material from incinerated ash of industrial waste and general waste - Google Patents
Method for producing burned material from incinerated ash of industrial waste and general wasteInfo
- Publication number
- JP3535334B2 JP3535334B2 JP01176597A JP1176597A JP3535334B2 JP 3535334 B2 JP3535334 B2 JP 3535334B2 JP 01176597 A JP01176597 A JP 01176597A JP 1176597 A JP1176597 A JP 1176597A JP 3535334 B2 JP3535334 B2 JP 3535334B2
- Authority
- JP
- Japan
- Prior art keywords
- waste
- water
- ash
- industrial waste
- quartz
- 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.)
- Expired - Lifetime
Links
Landscapes
- Compositions Of Oxide Ceramics (AREA)
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 burned material 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。Industrial waste and general waste are converted into 600 to 8
A method of incineration at a temperature of about 50 ° C and discarding the incinerated ash at the final disposal site for processing.
【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。Industrial waste and general waste are converted into 600 to 8
A method in which it is incinerated at a temperature of about 50 ° C, and the incinerated ash is solidified by adding a hardening material such as cement and water and aggregate to form 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。Industrial waste and general waste are converted into 600 to 8
A method of incinerating at a temperature of about 50 ° C. and converting the incinerated ash to molten slag at a higher temperature of about 1300 to 1800 ° C. The molten slag is used as an aggregate for cement concrete, an interblocking material that is crushed and molded and then re-fired, 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, in the above-mentioned conventional method, the following problems still remain.
【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 state of metals, oxides and chlorides, so that heavy metals are 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。The elution of such heavy metals and halogenated organic substances has a great influence on plants and animals in the natural world.
This may cause environmental damage that adversely affects the human body, and may cause a serious 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。Moreover, with the spread of the mass-consumption lifestyle in recent years, the amount of waste discharged tends to increase year by year.
Under these circumstances, the allowable number of years for final disposal sites owned by each local government is said to be about eight years. On the other hand, the construction of a new final disposal site by the local government has been slow to proceed due to problems such as selection / acquisition of the disposal site 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), since heavy metals and halogenated organic substances contained in the incineration ash remain in the cement concrete in the form of metals, oxides and chlorides, the method of cement concrete by rainwater or groundwater Water absorption
Due to the water permeation phenomenon, heavy metals and halogenated organic substances may elute outside the cement concrete, which may also cause environmental damage.
【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), heavy metals and halogenated organic substances contained in the incinerated ash are solid-soluted in the slag phase containing silicic acid as a main component, so that heavy metals and halogenated substances are affected by rainwater and groundwater. Organic substances, etc. will not elute in water. However, the apparatus for reburning incinerated ash to produce molten slag is expensive, at about 100 million yen per ton of incinerated ash,
Further, since the running cost is about 10,000 yen per ton of incinerated ash, it is difficult for local governments having financial difficulties to construct a treatment device.
【0012】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に、
水と、骨材としての石英と、アルミナセメントからなる
硬化材とを混合して得たスラリーを、あるいは産業廃棄
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、骨材とし
ての石英と、アルミナセメントからなる硬化材とを混合
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1200〜1260℃で焼成して焼成物を
得ることとした。そして、前記スラリーの混合比を、焼
却灰:石英:アルミナセメント:水=50〜60:40
〜50:30:50、及び焼却灰:火山灰:石英:アル
ミナセメント:水=30〜45:15〜30:40:3
0:50とした。An object of the present invention is to provide a method for producing a burned material using incineration ash of industrial waste and general waste, which can solve the above-mentioned problems. At least one of the incineration ash,
A slurry obtained by mixing water, quartz as aggregate, and a hardening material made of alumina cement, or incineration ash of at least one of industrial waste and general waste is mixed with volcanic deposits. A slurry obtained by mixing water, quartz as an aggregate, and a hardener made of alumina cement into the mixture is put into a mold to be solidified and molded, and then the molded product is 1200 to 1260 ° C. It was decided to obtain a fired product by firing at. Then, the mixing ratio of the slurry is set to incineration ash: quartz: alumina cement: water = 50 to 60:40.
~ 50: 30: 50, and incineration ash: volcanic ash: quartz: alumina cement: water = 30-45: 15-30: 40: 3
It was set to 0:50.
【0013】かかる方法により得られる焼成物は、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。The calcined product obtained by such a method is safe without elution of heavy metals and halogenated organic substances,
Moreover, the capital investment and the running cost for manufacturing this become 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 In the present invention, incineration ash of at least one of industrial waste and general waste is re-fired to be vitrified.
【0015】再焼成するに際しては、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
材としての石英と、アルミナセメントからなる硬化材と
を混合したスラリーを固化成形した成形物を、1200
〜1260℃で焼成することが好ましい。Upon re-firing, the incineration ash or a mixture of volcanic deposits mixed with water is mixed with water, quartz as an aggregate, and a hardening material made of alumina cement to be solidified and molded. Molded product 1200
It is preferable to bake at ˜1260 ° C.
【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 not eluted and the product can be directly made 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, the apparatus used has a feature that it does not require a treatment cost because existing kilns and equipment can be used.
【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 the heavy metals and halogenated organic substances contained in the incinerated ash can be enclosed in the fired product,
There is no elution to the outside due to rainwater or groundwater, there is no risk of causing environmental damage even if this is used for landfill, and even when this is disposed of at the final treatment site,
Since it is not necessary to spend enormous environmental destruction countermeasure costs in the final treatment plant, the treatment cost of industrial waste and general waste can be greatly reduced, which greatly contributes to the cost reduction of treatment companies and local governments.
【0019】しかも、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, since the fired product can be effectively used as a secondary product such as a water-permeable tile, a flower pot, a roof tile, a block for flower beds, a block for laying, and a block for fishing reefs, it is possible to open up a new market. 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。Since it has the characteristics of 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 incineration ash and the clay for pottery are made to have a weight ratio of 1: 1 and further dried by natural drying or by being hardened by adding a hardening material, 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 preferably used as the aggregate and alumina cement can be suitably used as the hardening agent. After naturally hardening in a mold having a desired shape, it is dried for a predetermined time (for example, 24 hours), and then, , 1230 ~ 1260 ℃
It is good to bake at the temperature of.
【0023】さらに、前記焼成物に、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。Furthermore, when a glaze is applied to the fired product and re-fired, 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 from each of 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。EXAMPLES Examples of the present invention will be specifically described below.
【0026】[0026]
【0027】(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 1) Industrial waste, general waste, or a mixture of both wastes was incinerated at a temperature of about 600 to 850 ° C, and the incinerated ash was used as a raw material. Granular quartz or fine quartz, alumina cement as a hardening material, and water were mixed to obtain a slurry.
【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 by weight ratio.
【0029】(1)焼却灰:粗粒石英:アルミナセメン
ト:水=50:50:30:50
(2)焼却灰:粗粒石英:アルミナセメント:水=6
0:40:30:50
(3)焼却灰:微粒石英:アルミナセメント:水=5
0:50:30:50
(4)焼却灰:微粒石英:アルミナセメント:水=6
0:40:30:50
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。(1) Incinerated ash: Coarse-grained quartz: Alumina cement: Water = 50: 50: 30: 50 (2) Incinerated ash: Coarse-grained quartz: Alumina cement: Water = 6
0: 40: 30: 50 (3) Incinerated ash: Fine quartz: Alumina cement: Water = 5
0: 50: 30: 50 (4) Incinerated ash: Fine quartz: Alumina cement: Water = 6
0: 40: 30: 50 The above-mentioned respective slurries were put into a predetermined mold, and each of them was charged with 2
After allowing it to stand at 5 ° C. for 24 hours for natural curing, 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 drier at 105 ° C. for one day and then calcined 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。At any temperature below 1150 ° C., the incinerated ash did not vitrify, so that the shape could not be retained, but at 1150 to 1200 ° C., a sintered body having a hardness like sandstone was formed, and 1200 to 1260 A glassy fired product having a robust hardness that did not break at some handling at ℃ was obtained.
【0032】[0032]
【0033】(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 2) Industrial waste, general waste, or a mixture of both wastes was incinerated at a temperature of about 600 to 850 ° C, and the incinerated ash was used as a raw material. Mix
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 weight ratios.
【0035】(1)焼却灰:火山灰:微粒石英:アルミ
ナセメント:水=45:15:40:30:50
(2)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。(1) Incinerated ash: Volcanic ash: Fine quartz: Alumina cement: Water = 45: 15: 40: 30: 50 (2) Incinerated ash: Volcanic ash: Fine quartz: Alumina cement:
Water = 30: 30: 40: 30: 50 The above-mentioned respective slurries are cast into a plate-shaped mold, and each is
After allowing it to stand at 5 ° C. for 24 hours for natural curing, 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 in a drier at 105 ° C. for one day and then calcined 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 is in the form of a tile which is firmly baked and solidified, and when the water is applied from the upper surface, it absorbs water, and when the amount of water is increased, a glassy fired product having a water permeability enough to drip from the lower surface is obtained. Was obtained.
【0038】(実施例3)
先の実施例2で得たガラス状焼成物に釉薬を塗布し、1
250℃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 3 A glaze was applied to the glass-like fired product obtained in Example 2 above, and 1
Rebaking at a temperature of 250 ° C. gave a glassy baked product with a glossy surface. It has been found that the inside is porous and lightweight, but has a property of impermeable to water because the glaze layer is 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 products obtained in each of the above examples can be filled with heavy metals and halogenated organic substances contained in incinerated ash in the glass and can be eluted to the outside by rainwater, groundwater, etc. Since there is no such thing, there is no danger of causing environmental damage even if it is filled up with land, and such a glassy fired product can be used as a functional product such as a water-permeable tile. It can be effectively used as a roof tile, a product such as a block for flower beds, a block for laying, a block for fish reefs, and also for a rubble stone for civil engineering.
【0040】また、実施例3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 3, the glass-like fired product to which glaze is applied 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, which is carried out in the above-described mode, has the following effects.
【0042】(1)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
に、水と、骨材としての石英と、アルミナセメントから
なる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1200〜1260℃
で焼成して得る産業廃棄物並びに一般廃棄物の焼却灰を
原料とする焼成物の製造方法であって、しかも、前記ス
ラリーの混合比を、焼却灰:石英:アルミナセメント:
水=50〜60:40〜50:30:50としている。
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して焼成物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
鉢や瓦、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
所望形状の二次製品として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。(1) In the present invention as set forth in claim 1, incineration ash of at least one of industrial waste and general waste is mixed with water, quartz as an aggregate, and a hardening material made of alumina cement. The obtained slurry is put into a mold to be solidified and molded, and then the molded product is 1200 to 1260 ° C.
A method for producing a burned material using incinerated ash of industrial waste and general waste obtained by firing as described above, wherein the mixing ratio of the slurry is incinerated ash: quartz: alumina cement:
Water = 50-60: 40-50: 30: 50.
Therefore, the heavy metals and halogenated organic substances contained in the incinerated ash can be enclosed in the vitreous material by enclosing it in the glass, and can be disposed of easily and safely,
This can be reused as functional products such as water-permeable tiles, and it is light and easy to handle and safe, so it is a flowerpot or tile, or a flowerbed block or laying block,
It can be effectively used as a secondary product having a desired shape for blocks for fish reefs, and also for rubble stones for civil engineering, which enables new market development and has a great economic levitation effect.
【0043】(2)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
に火山性堆積物を混合し、同混合物に、水と、骨材とし
ての石英と、アルミナセメントからなる硬化材とを混合
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1200〜1260℃で焼成して得る産業
廃棄物並びに一般廃棄物の焼却灰を原料とする焼成物の
製造方法であって、しかも、前記スラリーの混合比を、
焼却灰:火山灰:石英:アルミナセメント:水=30〜
45:15〜30:40:30:50としている。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して焼成物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鉢
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所
望形状の二次製品として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。(2) In the present invention according to claim 2, volcanic deposits are mixed with incineration ash of at least one of industrial waste and general waste, and the mixture is mixed with water and quartz as an aggregate. And a hardening agent made of alumina cement are mixed into a mold to be solidified and molded, and then the molded product is baked at 1200 to 1260 ° C to obtain industrial waste and general waste. A method for producing a fired product using incinerated ash as a raw material, wherein the mixing ratio of the slurry is
Incinerated ash: Volcanic ash: Quartz: Alumina cement: Water = 30〜
It is set to 45:15 to 30: 40: 30: 50. Therefore, the heavy metals and halogenated organic substances contained in the incinerated ash can be enclosed in the vitreous material by encapsulating it in the vitreous material, which can be easily and safely disposed of, and can be used as a function of a water-permeable tile or the like. Since it can be reused as a product, it is light and easy to handle and safe, so it can be used in flowerpots, roof tiles, flowerbed blocks, laying blocks, fish reef blocks, etc. It can be effectively used as a product, can open new markets, and has a great effect on the economy.
【0044】(3)請求項3記載の本発明では、成形物
を一度焼成した後の焼成物に、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。(3) According to the present invention as set forth in claim 3, the molded product is once baked, and the baked product is subjected to glaze and re-baked to be burned from incinerated ash of industrial waste and general waste as a raw material. I'm getting things. Therefore, although it has a porous interior, it has a glossy surface and is impervious to water, so it can be used as a lightweight ceramic substitute.
【0045】[0045]
───────────────────────────────────────────────────── フロントページの続き (72)発明者 迎 康範 長崎県北松浦郡佐々町須崎免506番地 (56)参考文献 特開 昭51−50921(JP,A) 特開 昭63−201055(JP,A) 特開 昭63−274650(JP,A) 特開 昭62−191457(JP,A) 特開 昭62−212260(JP,A) ─────────────────────────────────────────────────── ─── Continued front page (72) Inventor Yasunori 506 Susaki-Den, Sasa-cho, Kitamatsuura-gun, Nagasaki Prefecture (56) References Japanese Patent Laid-Open No. 51-50921 (JP, A) JP 63-201055 (JP, A) JP 63-274650 (JP, A) JP 62-191457 (JP, A) JP 62-212260 (JP, A)
Claims (3)
もいずれかの焼却灰に、水と、骨材としての石英と、ア
ルミナセメントからなる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1
200〜1260℃で焼成して得る産業廃棄物並びに一
般廃棄物の焼却灰を原料とする焼成物の製造方法であっ
て、前記スラリーの混合比を、 焼却灰:石英:アルミナセメント:水=50〜60:4
0〜50:30:50 とした 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焼成物の製造方法。1. A slurry obtained by mixing incineration ash of at least one of industrial waste and general waste with water , quartz as an aggregate, and a hardening material made of alumina cement is placed in a mold. Put it in and solidify it, then 1
That obtained by firing at 200~ 1260 ℃ industrial waste as well as single
It is a method of manufacturing a fired product that uses incineration ash of general waste as a raw material.
Then, the mixing ratio of the slurry is set to incineration ash: quartz: alumina cement: water = 50 to 60: 4.
0-50: 30: 50 and then a manufacturing method of industrial waste and incineration ash baked formed product shall be the raw material for general waste, characterized in that the.
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、骨材としての石英と、アルミナセメントから
なる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1200〜1260℃
で焼成して得る産業廃棄物並びに一般廃棄物の焼却灰を
原料とする焼成物の製造方法であって、前記スラリーの
混合比を、 焼却灰:火山灰:石英:アルミナセメント:水=30〜
45:15〜30:40:30:50 とした 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焼成物の製造方法。2. An incineration ash of at least one of industrial waste and general waste is mixed with a volcanic sediment, and the mixture is mixed with water, quartz as an aggregate, and a hardener made of alumina cement. The slurry obtained by mixing is put into a mold to be solidified and molded, and then the molded product is 1200 to 1260 ° C.
Incinerator ash of in industry that obtained by firing waste and general waste
A method for producing a fired product as a raw material, comprising:
Mixing ratio, Incinerated ash: Volcanic ash: Quartz: Alumina cement: Water = 30 ~
45: 15-30: 40: 30: 50 and then a manufacturing method of industrial waste and incineration ash baked formed product shall be the raw material for general waste, characterized in that the.
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焼成
物の製造方法。To 3. A baked formed product according to any one of claims 1 or 2, the incineration ash of industrial waste and general waste, characterized in that obtained by re-sintering after applying glaze to a raw material method of manufacturing a baked adult products that.
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 JPH10212154A (en) | 1998-08-11 |
JP3535334B2 true 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) |
Families Citing this family (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 |
CN102924090B (en) * | 2012-11-02 | 2014-10-29 | 佛山石湾鹰牌陶瓷有限公司 | Vitrified ceramic tile blank and vitrified ceramic tile preparation method thereof |
-
1997
- 1997-01-24 JP JP01176597A patent/JP3535334B2/en not_active Expired - Lifetime
Also Published As
Publication number | Publication date |
---|---|
JPH10212154A (en) | 1998-08-11 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
KR101198327B1 (en) | Method for Manufacturing Lightweight Construction Material Using Waste Sludge | |
KR100592781B1 (en) | Water-permeable concrete composition using bottom ash | |
Hegazy et al. | Reuse of water treatment sludge and silica fume in brick manufacturing | |
JP3188200B2 (en) | Manufacturing method of artificial lightweight aggregate | |
JP3535334B2 (en) | Method for producing burned material from incinerated ash of industrial waste and general waste | |
JPWO2006098202A1 (en) | Fired product | |
KR100971283B1 (en) | Stroll path and bicycleexclusive road pavement using natural materials | |
KR100450898B1 (en) | production of incinerated construction materials using wastewater sludge | |
KR20040080631A (en) | a | |
KR20120061607A (en) | A wrapping apparatus and the use method using sludge and natural ingredients | |
KR20120008557A (en) | Method for manufacturing standardization product by using sludge | |
KR20020043135A (en) | Concrete 2th production using mainly blast furance slag and waste gypsum | |
KR100468198B1 (en) | Construction material composition using foundry waste sand and method of producing construction material using the composition | |
KR100370268B1 (en) | The method of construction materials composition use for refuse lime | |
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 | |
KR102721947B1 (en) | Clay Brick composition and method of manufacturing the same | |
JP2000319048A (en) | Concrete product using hydraulic calcined product as binding material | |
KR100357524B1 (en) | Solidity material for reapplication of assignment waste harding foam having excellent compressive strength using the solidity material | |
RU2692340C1 (en) | Method of erecting an ellipsoidal enclosure wall (embankment) on landfill of ash utilization from combustion of sewage sludge | |
JP2009148752A (en) | Method for treating sludge or the like and water-sucking material of sludge | |
JP4155773B2 (en) | Cured body | |
JP2005035847A (en) | Method of recycling waste ceramic ware | |
JPH06144898A (en) | Mixed hydraulic substance, hardened material and burnt material | |
JPH1059765A (en) | Production of ceramic raw material and manufacture of ceramic tile by effectively utilizing molten slag of waste incineration ash |
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 |