JPH11157914A - Modification of ceramics using waste plastic - Google Patents
Modification of ceramics using waste plasticInfo
- Publication number
- JPH11157914A JPH11157914A JP34590797A JP34590797A JPH11157914A JP H11157914 A JPH11157914 A JP H11157914A JP 34590797 A JP34590797 A JP 34590797A JP 34590797 A JP34590797 A JP 34590797A JP H11157914 A JPH11157914 A JP H11157914A
- Authority
- JP
- Japan
- Prior art keywords
- waste plastic
- raw material
- waste
- clay
- ceramic
- 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
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/60—Production of ceramic materials or ceramic elements, e.g. substitution of clay or shale by alternative raw materials, e.g. ashes
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】この発明は廃プラスチックを
用いたセラミックスの改質方法に関する。[0001] The present invention relates to a method for modifying ceramics using waste plastic.
【0002】[0002]
【従来の技術】火力発電所から排出されるフライアッシ
ュ又は流動床灰等の石炭灰は、一部はセメント原料、合
成ゼオライト原料、土壌改良材等に利用されているが、
大半は産業廃棄物として埋め立てその他の方法でコスト
のかかる廃棄処分にまわされている。また、フライアッ
シュ等の化学組成は、セラミックス原料の組成に酷似し
ているため、以前からセラミックス原料の代替原料とし
て利用研究が行われて来たが、フライアッシュ等に含ま
れている未燃カーボンがセラミックスの焼成工程で燃焼
し、その際に発生するCO2、COガスが製品の品質や
生産性に大きく影響するため、ごく一部の無釉レンガ
(例えば、特許第1859617号)を除きほとんど使
用されていない。又、炭化物(木炭、石炭等)を含む粘
土、砂礫についても、同じように炭化物の燃焼ガスが製
品の品質に影響するため使用されていない。2. Description of the Related Art Coal ash such as fly ash or fluidized bed ash discharged from a thermal power plant is partially used as a raw material for cement, a raw material for synthetic zeolite, a soil conditioner, etc.
Most of the waste goes to landfills or other costly disposal as industrial waste. In addition, since the chemical composition of fly ash and the like is very similar to the composition of the ceramic raw material, utilization research has been conducted as an alternative raw material for the ceramic raw material, but the unburned carbon contained in the fly ash and the like has been studied. Is burned in the firing process of ceramics, and the CO 2 and CO gas generated at that time greatly affect the quality and productivity of the product. Therefore, almost all of the non-glazed bricks (eg, Patent No. 1859617) not being used. Similarly, clays and gravel containing carbides (charcoal, coal, etc.) are not used because the combustion gas of the carbides affects the quality of products.
【0003】[0003]
【発明が解決しようとする課題】フライアッシュ等の石
炭灰中に含まれる未燃カーボンや粘土、砂礫中に含まれ
る炭化物は、一般に400℃〜900℃位の間で燃焼す
る。一方、陶磁器等のセラミックス原料の主体をなす粘
土原料は、400℃付近から収縮を始め、900℃近辺
で急激に収縮する。そのため素地内部へ十分な酸素が供
給されず未燃カーボンや炭化物を含む原料ではこれらの
燃焼が非常に困難になり、燃焼は高温度領域(炉内温度
1000℃以上)まで継続する。釉薬を使用するセラミ
ックスでは燃焼反応が1000℃(炉内温度)以上にな
ると、燃焼ガス(CO2、CO)と溶融を始めた釉薬が
反応し、釉薬の色を変色させたり、表面にふくれや発泡
現象を起こしたりする。また、COガスは素地内部を還
元状態にさせるため、素地の中心部に黒芯(Black Cor
e)を発生させる。本発明が解決しようとする課題は、
このようなセラミックス製品表面の変色、ふくれ、発泡
現象や素地内部に生ずる黒芯現象等を除去することであ
る。The unburned carbon contained in coal ash, such as fly ash, and the carbide contained in clay and gravel generally burn between about 400 ° C. and 900 ° C. On the other hand, a clay raw material, which is a main component of ceramic raw materials such as ceramics, starts to shrink at around 400 ° C. and rapidly shrinks at around 900 ° C. For this reason, sufficient oxygen is not supplied to the inside of the substrate, and it becomes very difficult to burn these materials using unburned carbon or carbide, and the combustion continues to a high temperature region (a furnace temperature of 1000 ° C. or higher). In ceramics that use glaze, if the combustion reaction exceeds 1000 ° C (in-furnace temperature), the combustion gas (CO 2 , CO) reacts with the glaze that has begun to melt, changing the color of the glaze or causing blistering on the surface. It may cause a foaming phenomenon. In addition, CO gas causes the inside of the substrate to be in a reduced state.
e) occurs. The problem to be solved by the present invention is
The purpose of the present invention is to eliminate such discoloration, blistering, foaming phenomenon, black core phenomenon occurring inside the substrate, and the like on the surface of the ceramic product.
【0004】[0004]
【課題を解決するための手段】上記問題点を解決するた
めの本発明の方法は、第1に粘土を主成分とする窯業原
料に有機物を含む他の補助原料を添加したもの又は有機
物を含む粘土である窯業原料に対し適量の成形助材を加
えて混練した坏土を所定の形状に形成乾燥したものを焼
成する方法において、上記配合原料に廃プラスチックを
添加し、焼成過程において低温下で上記廃プラスチック
の燃焼とともに前記有機物を燃焼させて焼失せしめるこ
とを特徴としている。According to the method of the present invention for solving the above-mentioned problems, first, a ceramic raw material containing clay as a main component and another auxiliary raw material containing an organic substance added thereto or containing an organic substance are contained. In a method in which an appropriate amount of a molding aid is added to a ceramic raw material that is clay, a kneaded clay is formed into a predetermined shape, and then dried and fired, a waste plastic is added to the compounded raw material, and the firing process is performed at a low temperature. It is characterized in that the organic matter is burned and burned off together with the burning of the waste plastic.
【0005】第2に補助原料が石炭灰であることを特徴
としている。[0005] Second, the auxiliary raw material is coal ash.
【0006】第3に廃プラスチックが170〜450℃
の低温領域で熱分解と燃焼が可能なものであることを特
徴としている。Third, waste plastic is 170-450 ° C.
It is characterized in that it can be thermally decomposed and burned in a low temperature range.
【0007】第4に添加される廃プラスチックがプラス
チック廃材を粉砕した粉体又は粒状体であることを特徴
としている。Fourthly, the waste plastic to be added is characterized in that it is a powder or a granular material obtained by pulverizing a plastic waste material.
【0008】[0008]
【発明の実施の形態】本発明は、セラミックス製品の製
造に際しセラミックス(窯業)原料と未燃カーボンやそ
の他の炭化物等の有機物を含む粉体や粘土を配合した原
料に、低温領域(170〜450℃)で熱分解と燃焼が
可能な廃プラスチックを添加することにより、有機物に
よって生じるセラミックス製品の欠点を解消する改質方
法に関するものである。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention relates to a ceramic (ceramic) raw material and a raw material obtained by mixing a powder or a clay containing organic substances such as unburned carbon and other carbides in the production of ceramic products. The present invention relates to a reforming method for eliminating the drawbacks of ceramic products caused by organic substances by adding waste plastics that can be thermally decomposed and burned at (° C).
【0009】添加された廃プラスチックは、素地焼成中
に熱分解と燃焼を行うが、その際素地の中に小さな孔を
生じさせ、又燃焼熱(6200〜1100Kcal/Kg)が
素地内部の温度を上昇させる。そのため、原料中に含ま
れる未燃カーボンやその他の炭化物等の有機物は低温領
域で完全燃焼させることが可能となり、有機物の燃焼ガ
ス(CO、CO2)が作用して生ずるセラミックス製品
表面の欠陥(変色、あばた)及び素地内部に生ずる黒芯
を防止させることが可能となる。The added waste plastic undergoes thermal decomposition and combustion during firing of the green body. At that time, small holes are formed in the green body, and the heat of combustion (6200 to 1100 Kcal / Kg) reduces the temperature inside the green body. To raise. Therefore, organic substances such as unburned carbon and other carbides contained in the raw material can be completely burned in a low-temperature region, and defects (such as defects on the surface of a ceramic product caused by the action of organic combustion gas (CO, CO 2 )). It is possible to prevent discoloration, pocking) and a black core generated inside the substrate.
【0010】本発明の特徴は、有機物を多く含むため、
セラミックス原料として使用し難い、又使用出来ない有
機物を含む粉体、粘土等をセラミックス代替原料として
利用可能にさせることである。次に本発明の具体的な実
施例につき詳述すると、以下の実施例では粘土からなる
窯業原料にフライアッシュ,炭化物,もみ穀炭を添加し
た場合をそれぞれ実施例1〜4として示す。なお、原料
中に添加したプラスチックはいずれも粉体又は細粒状に
粉砕された粒状のものを使用した。The feature of the present invention is that it contains a large amount of organic substances,
An object of the present invention is to make it possible to use powders, clays, and the like containing organic substances that are difficult to use as ceramic raw materials and that cannot be used as ceramic raw materials. Next, specific examples of the present invention will be described in detail. In the following examples, examples in which fly ash, carbide, and fir coal are added to a ceramic raw material made of clay are shown as Examples 1 to 4, respectively. The plastics added to the raw materials were all powdered or finely pulverized.
【0011】実施例1) 74μ篩通過率95%の粉砕窯業原料(粘土鉱物、石
英、長石、雲母鉱物)に未燃カーボン含有量6%のフラ
イアッシュを重量比で42%添加して作成し、施釉した
テストピースA1(150mm×40mm×20mm)と同原
料に同種、同量のフライアッシュと粉砕されたメタクリ
ル樹脂を重量比16%添加して作成し、施釉したテスト
ピースB1(150mm×40mm×20mm)を瓦焼成用ト
ンネル炉に入れ、昇温速度300℃/hで焼成した。そ
の結果、テストピースA1には素地内部全体にわたり黒
芯が認められ、又釉面にはピンホールが発生した。一
方、テストピースB1は、A1に比較し重量がやや減少
したが、未燃カーボンによる異常は一切認められず、素
地も白色を呈した。Example 1) A raw material was prepared by adding 42% by weight of fly ash containing 6% of unburned carbon to a pulverized ceramic raw material (clay mineral, quartz, feldspar, mica mineral) having a passing rate of 74% through a 74μ sieve. , glazed and test piece a 1 (150mm × 40mm × 20mm ) and allogeneic the same raw material, prepared by adding the same amount of fly ash and pulverized methacrylic resin weight ratio 16%, glazed and test piece B 1 (150 mm (× 40 mm × 20 mm) was placed in a tunnel furnace for firing tiles and fired at a rate of temperature rise of 300 ° C./h. As a result, the black core was observed over the entire inner matrix is in the test piece A 1, also pinhole occurs in釉面. On the other hand, test piece B 1 represents, but weight compared to A 1 is decreased slightly, abnormality due to the unburned carbon is not observed at all, the matrix also exhibited white.
【0012】実施例2) 74μ篩通過率95%の粉砕窯業原料(粘土鉱物、石
英、長石、雲母鉱物)に未燃カーボン含有量6%のフラ
イアッシュを重量比で40%添加して作成し、施釉した
テストピースA2(150mm×40mm×20mm)と同原
料に同種、同量の炭化物と粉砕されたポリスチレンを重
量比16%添加して作成し、施釉したテストピースB2
(150mm×40mm×20mm)を電気炉に入れ、昇温速
度300℃/hで焼成した。その結果、テストピースA
2には素地内部に厚さ10mm黒芯が認められ、又釉面に
はピンホールが発生した。一方、テストピースB2は、
A2に比較し重量がやや減少したが、未燃カーボンによ
る異常は一切認められず、素地色も白色を呈した。Example 2) A crushed ceramic raw material (clay mineral, quartz, feldspar, mica mineral) having a passing rate of 74% through a 74μ sieve was prepared by adding 40% by weight of fly ash having an unburned carbon content of 6%. A test piece B 2 made by adding the same material, the same amount of carbide and crushed polystyrene to the same raw material as the glazed test piece A 2 (150 mm × 40 mm × 20 mm) by 16% by weight,
(150 mm × 40 mm × 20 mm) was placed in an electric furnace and fired at a heating rate of 300 ° C./h. As a result, test piece A
In No. 2 , a black core having a thickness of 10 mm was recognized inside the substrate, and a pinhole was generated on the glaze surface. On the other hand, test piece B 2
Although weight compared to the A 2 is decreased slightly, abnormality due to the unburned carbon is not observed at all, foundation colors also white in color.
【0013】実施例3) 74μ篩通過率95%の粉砕窯業原料に、「もみ殻炭」
を重量比で5%添加して湿式成形したテストピースA3
(40mm×20mm×150mm)、及び同粉砕原料に重量
比5%の「もみ殻炭」と重量比5%のアクリル樹脂を添
加して湿式成形したテストピースB3(40mm×20mm
×150mm)の表面に施釉した後、共に電気炉を用い
て、昇温速度300℃/hで1200℃焼成した。この
焼成したテストピースの中央部を切断して内部を観察す
ると、テストピースA3は全面が黒色を呈し、テストピ
ースB3はほぼ白色で黒芯が全く認められなかった。Example 3) Rice husk charcoal was used as a raw material for pulverized ceramics with a passing rate of 74% through a 74μ sieve.
The added 5% by weight test piece A 3 was wet-molded
(40 mm × 20 mm × 150 mm) and a test piece B 3 (40 mm × 20 mm) which was wet-formed by adding 5% by weight of “rice husk charcoal” and 5% by weight of acrylic resin to the ground material.
X150 mm), and then baked at 1200 ° C at a rate of 300 ° C / h using an electric furnace. When observing the inside by cutting the central portion of the fired test pieces, test piece A 3 is the entire surface of a black color, the test piece B 3 was completely observed black core almost white.
【0014】以上の結果を考察するに、炭化物含有の原
料に適量の廃プラスチック材を添加して焼成すると、廃
プラスチック類(特に熱可塑性樹脂等)は、焼成過程で
分解温度(170〜450℃)以下の比較的低温度で溶
融(吸熱反応)して、粘土に吸着された後、分解温度領
域で揮発、燃焼(燃焼熱 6200〜11000Kcal/
Kg)を行う。このため溶融物が存在した跡は、小さな孔
が開いた多孔質状態になり、素地内部の空気や分解ガス
の拡散が促進させられ、又分解ガスの燃焼により素地内
部の温度が上昇する。それにより、その後に起きる素地
中に含まれる炭化物、未燃カーボン等の燃焼が非常に容
易になり、炭化物、未燃カーボン等の有機物の燃焼反応
が、1000℃迄にほとんど終了し、燃焼ガスはセラミ
ックス製品の品質に全く影響しない。Considering the above results, when an appropriate amount of waste plastic material is added to a carbide-containing raw material and fired, the waste plastics (particularly, thermoplastic resin and the like) are decomposed at a decomposition temperature (170 to 450 ° C.) during the firing process. ) Melts (endothermic reaction) at relatively low temperature below and is adsorbed by clay, then volatilizes and burns (combustion heat 6200-11000 Kcal /
Kg). For this reason, the trace of the presence of the melt becomes a porous state in which small holes are opened, the diffusion of the air and the decomposition gas inside the base material is promoted, and the temperature inside the base material increases due to the combustion of the decomposition gas. As a result, the subsequent combustion of carbides, unburned carbon and the like contained in the base material becomes very easy, and the combustion reaction of the organic matter such as carbides and unburned carbon is almost completed by 1000 ° C. Has no effect on the quality of ceramic products.
【0015】これに対し廃プラスチックを添加しないも
のでは、焼成途中の素材収縮等もあって、炭化物等の燃
焼が不十分になり、内部の黒芯の発生や釉薬溶融開始後
の燃焼継続による変色や発泡現象が避けられないという
問題を生じることが判明した。また素材中に含まれる可
燃物はフライアッシュの未燃カーボンに限られず、実施
例で示した各種の炭化物等のほか、広く有機物一般に対
して適用可能である。On the other hand, in the case where no waste plastic is added, the burning of carbides and the like becomes insufficient due to the shrinkage of the material during the firing, the generation of a black core inside, and the discoloration due to the continued burning after the start of melting the glaze. It has been found that a problem that the foaming phenomenon cannot be avoided is caused. Further, the combustibles contained in the material are not limited to unburned carbon of fly ash, and can be widely applied to general organic substances in addition to the various carbides shown in the examples.
【0016】その他廃プラスチックの材質としては、上
述したメタクリル(アクリル)樹脂(PMMA),ポリ
スチレン樹脂(PS)のほか、概ね170〜450℃の
低温領域で熱分解又は燃焼するポリプロピレン(P
P),ポリエチレン(PE),ABS樹脂,不飽和ポリ
エステル樹脂(UP)等の使用が可能であり、これらの
廃プラスチック利用は廃棄物利用による廃棄処理コスト
及び原料単価の面で二重のコストメリットが達成できる
利点がある。Other materials for the waste plastic include methacryl (acrylic) resin (PMMA) and polystyrene resin (PS), as well as polypropylene (P) which thermally decomposes or burns at a low temperature of about 170 to 450 ° C.
P), polyethylene (PE), ABS resin, unsaturated polyester resin (UP), etc. can be used, and the use of these waste plastics is a double cost merit in terms of waste disposal cost and raw material unit cost by using waste. There are advantages that can be achieved.
【0017】[0017]
【発明の効果】以上のように構成される本発明によれ
ば、多量に排出される産業廃棄物等の廃棄物であるフラ
イアッシュや流動床灰、その他セラミックス材料として
は品質不良とされる有機物含有の窯業原料を実用可能な
セラミックス製品の原料として有効利用できるともに、
これらの改良を同じく廃棄物である廃プラスチックの有
効利用により実現できるという処理コスト及び材料コス
トの両面で優れた経済性をもたらす効果がある。According to the present invention constructed as described above, fly ash and fluidized bed ash which are wastes such as industrial wastes discharged in large quantities, and other organic substances which are of poor quality as ceramic materials Contained ceramic materials can be effectively used as raw materials for practical ceramic products,
These improvements can be realized by the effective use of waste plastics, which is also a waste, which has the effect of providing excellent economics in both processing costs and material costs.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 村田 豊 島根県江津市都野津町1268 株式会社ヨー ケン内 (72)発明者 新田 隆義 島根県江津市都野津町1268 株式会社ヨー ケン内 (72)発明者 平岩 国彦 島根県江津市都野津町1268 株式会社ヨー ケン内 (72)発明者 前田 禎彦 神奈川県横浜市鶴見区上の宮1−16−8− 301 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Yutaka Murata 1268, Tsunozu-cho, Gotsu-shi, Shimane Prefecture Inside Yoken Co., Ltd. Person Kunihiko Hiraiwa 1268 Tsunozu-cho, Gotsu City, Shimane Prefecture Inside Yoken Co., Ltd. (72) Inventor Yoshihiko Maeda 1-16-8-301 Kamimiya, Tsurumi-ku, Yokohama
Claims (4)
含む他の補助原料を添加したもの又は有機物を含む粘土
である窯業原料に対し適量の成形助剤を加えて混練した
坏土を所定の形状に形成乾燥したものを焼成する方法に
おいて、上記配合原料に廃プラスチックを添加し、焼成
過程において低温下で上記廃プラスチックの燃焼ととも
に前記有機物を燃焼させて焼失せしめる廃プラスチック
を用いたセラミックスの改質方法。1. A kneaded clay obtained by adding an appropriate amount of a molding aid to a ceramic raw material containing clay as a main component and adding an auxiliary material containing an organic substance to a ceramic raw material containing the clay or an auxiliary material containing an organic substance. In the method of firing the formed and dried product in the shape of, a waste plastic is added to the compounding raw material, and the waste plastic is burned and burned down by burning the organic matter together with the waste plastic at a low temperature in a firing process. Reforming method.
ラスチックを用いたセラミックスの改質方法。2. The method according to claim 1, wherein the auxiliary raw material is coal ash.
温領域で熱分解と燃焼が可能なものである請求項1又は
2の廃プラスチックを用いたセラミックスの改質方法。3. The method for modifying ceramics using waste plastic according to claim 1, wherein the waste plastic can be thermally decomposed and burned in a low temperature range of 170 to 450 ° C.
ク廃材を粉砕した粉体又は粒状体である請求項1又は2
又は3の廃プラスチックを用いたセラミックスの改質方
法。4. The waste plastic to be added is a powder or granules obtained by pulverizing plastic waste.
Or a method for modifying ceramics using waste plastics of 3.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP34590797A JPH11157914A (en) | 1997-12-01 | 1997-12-01 | Modification of ceramics using waste plastic |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP34590797A JPH11157914A (en) | 1997-12-01 | 1997-12-01 | Modification of ceramics using waste plastic |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH11157914A true JPH11157914A (en) | 1999-06-15 |
Family
ID=18379810
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP34590797A Pending JPH11157914A (en) | 1997-12-01 | 1997-12-01 | Modification of ceramics using waste plastic |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH11157914A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101149746B1 (en) | 2010-03-12 | 2012-06-01 | 주식회사 에코디텍 | Resin Composition for Block Including Bottom Ash and the Block |
CN102503366A (en) * | 2011-10-08 | 2012-06-20 | 金立虎 | Method for manufacturing gold tailings ash aggregates |
-
1997
- 1997-12-01 JP JP34590797A patent/JPH11157914A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101149746B1 (en) | 2010-03-12 | 2012-06-01 | 주식회사 에코디텍 | Resin Composition for Block Including Bottom Ash and the Block |
CN102503366A (en) * | 2011-10-08 | 2012-06-20 | 金立虎 | Method for manufacturing gold tailings ash aggregates |
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