JPS5836969A - Bake binding method for waste burned ash - Google Patents

Bake binding method for waste burned ash

Info

Publication number
JPS5836969A
JPS5836969A JP56131476A JP13147681A JPS5836969A JP S5836969 A JPS5836969 A JP S5836969A JP 56131476 A JP56131476 A JP 56131476A JP 13147681 A JP13147681 A JP 13147681A JP S5836969 A JPS5836969 A JP S5836969A
Authority
JP
Japan
Prior art keywords
ash
waste
bake
binding method
clay
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
JP56131476A
Other languages
Japanese (ja)
Inventor
樋 幸四郎
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 JP56131476A priority Critical patent/JPS5836969A/en
Publication of JPS5836969A publication Critical patent/JPS5836969A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/60Production of ceramic materials or ceramic elements, e.g. substitution of clay or shale by alternative raw materials, e.g. ashes

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Compositions Of Oxide Ceramics (AREA)

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 この発明は、一般廃棄物,産業廃棄物,汚泥などの焼却
灰、および集じん灰と可塑性粘土,陶石,SiO2,K
2O3・Al203・6SiO2,Na2O・Al2O
3・6SiO2,Al2O3・2SiO2・2H2O,
Al2O3・4SiO2・H2O等を焼却灰の性状に応
じて適宜混合調製して混練したのち成型し、焼成により
熔化結合を計り、陶器質化、■器質化、磁器質化による
廃棄物の再資源化に関する。
DETAILED DESCRIPTION OF THE INVENTION This invention uses incinerated ash such as general waste, industrial waste, and sludge, and collected ash, plastic clay, pottery stone, SiO2, K
2O3・Al203・6SiO2, Na2O・Al2O
3.6SiO2, Al2O3.2SiO2.2H2O,
After mixing and kneading Al2O3, 4SiO2, H2O, etc. according to the properties of the incineration ash, it is molded, and the melting bond is measured by firing, and the waste is recycled by making it into ceramic, ■organizing, and porcelain. Regarding.

従来の廃棄物対策は、一部の金属類、故紙類、ガラス類
の再資源化に限られ、大部分は最終的に原始的埋立法に
頼るしかなく、埋立てを容易にするための前処理として
焼却、分解、結合などの操作を施してきた。
Conventional waste countermeasures are limited to the recycling of some metals, waste paper, and glass, and most of them ultimately have to rely on primitive landfill methods, with the aim of making landfill easier. Treatments include incineration, decomposition, and combination.

しかし、これらの廃棄物処理法には、埋立地の制限、埋
立てによる将来の環境におよぼす副次的影響、埋立てに
費す多額の経費等の多くの問題が山積している。
However, these waste disposal methods are fraught with many problems, such as limited landfill space, the side effects of landfilling on the future environment, and the large amount of expense spent on landfilling.

以上の状況から、廃棄物の再資源化は今時の最大の課題
である。
Given the above circumstances, waste recycling is the biggest issue of our time.

但し、廃棄物の処理や再資源化に際して十分留意しなけ
ればならないことは、処理、再資源化にあたり副次的な
第二次環境汚染を誘発する恐れがないこと、再資源化製
品は、品質的に優れていること、製品コストが低廉であ
ること、利用者が再資源化製品を十分理解し愛用できる
ことなどである。
However, when processing and recycling waste, it is necessary to pay close attention to the fact that there is no risk of secondary environmental pollution occurring during processing and recycling, and that recycled products are of high quality. These include the fact that recycled products are superior in quality, their product costs are low, and users can fully understand and use recycled products.

この発明は、以上の条件を十分満たすことのできる廃棄
物の再資源化を目的とした。
This invention aims at recycling waste that fully satisfies the above conditions.

この発明を実施した実施例を図にもとづいて説明すると
次の通りである。
An embodiment of the present invention will be described below based on the drawings.

焼却炉から排出した焼却灰を図A,Bの工程によって篩
別し、Meshes60以下の微細粉を水洗し未燃物等
の不純物を除去して、精製微細粉灰とする。
The incinerated ash discharged from the incinerator is sieved through the steps shown in Figures A and B, and the fine powder with a mesh size of 60 or less is washed with water to remove impurities such as unburned materials, resulting in purified fine powder ash.

また、陶石、SiO2,K2O・Al2O3・6SiO
2,Na2O・Al2O3・6SiO2,Al2O3・
2SiO2・2H2O,Al2O3・4SiO2・H2
Oは、不純物を除去して水洗いしたのち粗砕する。次に
図Cの工程、ボールミルに送り20〜24時間微粉砕を
おこなう。そののち精製微細灰ならびに可塑性粘土を加
えて、3〜5時間粉砕と混合をおこない泥漿とする。
Also, pottery stone, SiO2, K2O・Al2O3・6SiO
2, Na2O・Al2O3・6SiO2, Al2O3・
2SiO2・2H2O, Al2O3・4SiO2・H2
O is crushed after removing impurities and washing with water. Next, in the step shown in Figure C, the mixture is sent to a ball mill and pulverized for 20 to 24 hours. Thereafter, purified fine ash and plastic clay are added, and the mixture is ground and mixed for 3 to 5 hours to form a slurry.

ボールミルから取出した泥漿は、図D,E,F,Gの工
程順序に従って篩別(Meshes60以下)し、水簸
したのち電磁選により脱鉄をおこなう。
The slurry taken out from the ball mill is sieved (Meshes 60 or less) according to the process order shown in Figures D, E, F, and G, and after elutriation, iron is removed by electromagnetic separation.

次にフィルタープレスに送り脱水してケーキを得る。Next, it is sent to a filter press and dehydrated to obtain a cake.

ケーキは、真空土練機を通して混練と脱気とをおこなっ
て坏土とした。
The cake was kneaded and degassed through a vacuum kneading machine to form clay.

坏土の組成によって焼成温度を異にし、適応製品も異に
するので、坏土の混合組成実用例を表1に示した。
Since the firing temperature and applicable products are different depending on the composition of the clay, Table 1 shows practical examples of mixed compositions of the clay.

成型は、60kg/cm2以上でプレス成型し、室温で
乾燥する。室温25℃であれば120時間で水分は完全
に除去できる。
The molding is performed by press molding at 60 kg/cm2 or more and dried at room temperature. At room temperature of 25°C, moisture can be completely removed in 120 hours.

十分乾燥したのち、焼成炉に送り焼成する。After it is sufficiently dried, it is sent to a kiln and fired.

焼成は1時間150℃前後の温度上昇速度が適当であり
、焼成結合温度に達したら火を止め、徐々に冷却して製
品を獲得する。
A temperature increase rate of around 150° C. for 1 hour is suitable for firing, and when the firing bonding temperature is reached, the fire is stopped and the product is obtained by gradually cooling.

表1 坏土組成・焼成温度・適応製品 一般廃棄物焼却灰の性状は、FeO3,TiO,CaO
ZnO3,SiO2,K2O,MgOなどが主であって
、Al2O3は比較的少ない傾向にあるので、Al2O
3の含有量の多い粘土を使用するか、または、化学薬品
のAl2O3を加える場合もある。
Table 1 Clay composition, firing temperature, applicable products The properties of general waste incineration ash are FeO3, TiO, CaO
Mainly ZnO3, SiO2, K2O, MgO, etc., and Al2O3 tends to be relatively small, so Al2O
In some cases, clay with a high content of 3 is used, or the chemical Al2O3 is added.

産業廃棄物焼却灰は主に「鉱さい」であり、陶磁器材料
には有利に利用される。
Industrial waste incineration ash is mainly "mine slag" and is advantageously used for ceramic materials.

また、この発明の実施による製品について、タイルの場
合の日本工業規格試験結果は、表2に示した。試験結果
は規格品として十分な結果であった。
Table 2 shows the results of the Japanese Industrial Standards test for tiles for products according to the present invention. The test results were sufficient for a standard product.

表2 JIS A−5209の試験結果Table 2 JIS A-5209 test results

【図面の簡単な説明】[Brief explanation of the drawing]

図は、この発明の実施にあたり、製法工程を示したもの
である。 製法で重要なポイントは、坏土の混合組成と焼成温度で
ある。
The figure shows the manufacturing process for carrying out this invention. Important points in the manufacturing method are the mixture composition of the clay and the firing temperature.

Claims (1)

【特許請求の範囲】[Claims] 1.廃棄物焼却灰微細粉と粘土,陶石,石英,長石,珪
石,カオリン等の鉱物微細粉を混練し、焼成熔融結合に
よる陶磁製品の製法2.特許請求の範囲第1項記載の焼
却灰は、一般廃棄物焼却灰,産業廃棄物焼却灰、汚泥焼
却灰、集じん灰におよぶものである。
1. A method for manufacturing ceramic products by kneading waste incineration ash fine powder and mineral fine powder such as clay, pottery stone, quartz, feldspar, silica stone, kaolin, etc., and firing and fusion bonding 2. The incinerated ash described in claim 1 includes general waste incinerated ash, industrial waste incinerated ash, sludge incinerated ash, and collected ash.
JP56131476A 1981-08-24 1981-08-24 Bake binding method for waste burned ash Pending JPS5836969A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56131476A JPS5836969A (en) 1981-08-24 1981-08-24 Bake binding method for waste burned ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56131476A JPS5836969A (en) 1981-08-24 1981-08-24 Bake binding method for waste burned ash

Publications (1)

Publication Number Publication Date
JPS5836969A true JPS5836969A (en) 1983-03-04

Family

ID=15058860

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56131476A Pending JPS5836969A (en) 1981-08-24 1981-08-24 Bake binding method for waste burned ash

Country Status (1)

Country Link
JP (1) JPS5836969A (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62136540U (en) * 1986-02-20 1987-08-28
JPH02175204A (en) * 1988-12-28 1990-07-06 Shin Nippon Kanetsu Kako Kk Manufacture of burnt matter by making use of burnt ash
JPH0558707A (en) * 1991-09-06 1993-03-09 Art Ceramic Kk Production of artificial stone or tile utilizing wastes
JPH0578161A (en) * 1985-10-24 1993-03-30 Fujimi Ceramic Kk Treatment of sewage sludge
JPH0672754A (en) * 1992-07-08 1994-03-15 Iwafuku Ceramics:Kk Production of brick
JPH0717756A (en) * 1993-06-30 1995-01-20 Tenmeizan Fudouin Kaigohouji Earthenware into which residual ash component of holy fire is incorporated and its production
EP1215182A1 (en) * 2000-12-13 2002-06-19 ECO Conception Conseil Ceramic based on household waste incineration slag
WO2003043753A1 (en) * 2001-11-21 2003-05-30 Art Ceramic Co., Ltd. Method for producing granules containing harmful substance from incineration ash or the like
CN106630932A (en) * 2016-10-17 2017-05-10 惠达卫浴股份有限公司 Slurry specially used for high-pressure molding, and producing and using methods thereof

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0578161A (en) * 1985-10-24 1993-03-30 Fujimi Ceramic Kk Treatment of sewage sludge
JPS62136540U (en) * 1986-02-20 1987-08-28
JPH02175204A (en) * 1988-12-28 1990-07-06 Shin Nippon Kanetsu Kako Kk Manufacture of burnt matter by making use of burnt ash
JPH0558707A (en) * 1991-09-06 1993-03-09 Art Ceramic Kk Production of artificial stone or tile utilizing wastes
JPH0672754A (en) * 1992-07-08 1994-03-15 Iwafuku Ceramics:Kk Production of brick
JPH0717756A (en) * 1993-06-30 1995-01-20 Tenmeizan Fudouin Kaigohouji Earthenware into which residual ash component of holy fire is incorporated and its production
EP1215182A1 (en) * 2000-12-13 2002-06-19 ECO Conception Conseil Ceramic based on household waste incineration slag
WO2003043753A1 (en) * 2001-11-21 2003-05-30 Art Ceramic Co., Ltd. Method for producing granules containing harmful substance from incineration ash or the like
CN106630932A (en) * 2016-10-17 2017-05-10 惠达卫浴股份有限公司 Slurry specially used for high-pressure molding, and producing and using methods thereof
CN106630932B (en) * 2016-10-17 2019-12-10 惠达卫浴股份有限公司 Special slurry for high-pressure forming and preparation and use methods thereof

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