JPH0829313B2 - Manufacturing method of ceramic raw materials and manufacturing method of fired products using incinerated ash of municipal waste - Google Patents

Manufacturing method of ceramic raw materials and manufacturing method of fired products using incinerated ash of municipal waste

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Publication number
JPH0829313B2
JPH0829313B2 JP3259673A JP25967391A JPH0829313B2 JP H0829313 B2 JPH0829313 B2 JP H0829313B2 JP 3259673 A JP3259673 A JP 3259673A JP 25967391 A JP25967391 A JP 25967391A JP H0829313 B2 JPH0829313 B2 JP H0829313B2
Authority
JP
Japan
Prior art keywords
manufacturing
ceramic raw
municipal waste
incineration ash
raw materials
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
Application number
JP3259673A
Other languages
Japanese (ja)
Other versions
JPH0568959A (en
Inventor
節一 笠井
計爾 小川
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.)
MINO SHIGEN KAIHATSU JUGEN
Kubota Corp
Original Assignee
MINO SHIGEN KAIHATSU JUGEN
Kubota Corp
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 MINO SHIGEN KAIHATSU JUGEN, Kubota Corp filed Critical MINO SHIGEN KAIHATSU JUGEN
Priority to JP3259673A priority Critical patent/JPH0829313B2/en
Publication of JPH0568959A publication Critical patent/JPH0568959A/en
Publication of JPH0829313B2 publication Critical patent/JPH0829313B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、都市ごみを焼却するこ
とによつて生じる灰を無公害化し、窯業原料を製造する
方法及びその方法によって得られた窯業原料を用いて焼
成品を製造する方法に関する。
BACKGROUND OF THE INVENTION The present invention relates to a method for producing a ceramic raw material by making ash produced by incinerating municipal solid waste non-polluting, and a ceramic raw material obtained by the method.
The present invention relates to a method of manufacturing a product .

【0002】[0002]

【従来の技術】都市ごみは近年、急激に増加し、その処
理が問題となっている。都市ごみのうち可燃物はそのま
ま埋め立てられるほか、焼却して廃棄処分されている。
しかしながら、都市ごみ焼却灰には、窒素、硫黄、塩素
等の各種化合物が複雑な形で存在するため石灰、ソーダ
等を混入することにより中和して無公害化しているが、
時間の経過とともに分解して二次公害が発生する。これ
を解決する有効な技術は未だ開発されていない。
2. Description of the Related Art Municipal solid waste has increased rapidly in recent years, and its disposal has become a problem. Combustibles in municipal waste are landfilled as they are, or incinerated and disposed of.
However, since various compounds such as nitrogen, sulfur, and chlorine are present in a complicated form in the incinerated ash of municipal waste, it is neutralized by mixing lime, soda, etc.
It decomposes over time and secondary pollution occurs. An effective technique for solving this has not been developed yet.

【0003】[0003]

【発明が解決しようとする課題】本発明が解決しようと
する課題は、都市ごみ焼却灰を無公害化し、窯業原料と
して利用することにある。
The problem to be solved by the present invention is to make municipal waste incineration ash pollution-free and utilize it as a raw material for ceramics.

【0004】[0004]

【課題を解決するための手段】のような課題を解決す
るための手段として、請求項1の発明は、都市ごみ焼却
灰を熔融するまで加熱し、冷却して得られたスラグを粉
砕する構成とし、また、請求項2の発明は、都市ごみ焼
却灰に下水道汚泥等の廃棄物を混合して熔融する構成と
、さらに、請求項3の発明は、請求項1または請求項
2記載の窯業原料の製造方法において得られた窯業原料
と窯業原料成分調整材とを水とともに混合混練して製品
形状に成型し、成形品を整燥後に800℃〜1110℃
で焼成することにより焼成品を製造する構成とした。
As a means for solving the problem as this Means for Solving the Problems] The invention of claim 1, heated to melt the municipal waste incineration ash, pulverized slag obtained by cooling configuration and then, also, the invention of claim 2, and configured to melt a mixture of wastes such as sewage sludge municipal waste incineration ash, furthermore, the invention of claim 3, claim 1 or claim
Ceramic raw materials obtained by the method for manufacturing ceramic raw materials according to 2.
The product is made by mixing and kneading the raw material composition adjusting material for ceramics with water.
800 ℃ ~ 1110 ℃ after molding into a shape and drying the molded product
It was configured to produce a fired product by firing at.

【0005】[0005]

【発明の作用及び効果】このスラグは一旦熔融している
ため嵩が小さくなり嵩比が安定する。しかも、完全燃焼
のため臭いの発生もなく、また、PCBなどの難分解性
塩基化合物も分解されるので二次公害の発生もない。熔
融の際に発生する排ガスはソーダで中和することにより
安定した塩等に再生される。したがつて、焼却灰は無公
害化される。
The function and effect of the present invention: Since this slag is once melted, the bulk becomes small and the bulk ratio becomes stable. Moreover, no odor is generated due to the complete combustion, and no secondary pollution is caused because the hardly decomposable basic compound such as PCB is decomposed. Exhaust gas generated during melting is regenerated into stable salt by neutralizing with soda. Therefore, the incineration ash is made pollution-free.

【0006】スラグの成分は都市ごみの発生場所によつ
て異なるが、ある一定の範囲にあり、陶磁器の釉薬に似
ているため、従来の窯業原料と同じような利用が可能
で、単独または従来の窯業原料と組み合わせ、温度を様
々に設定することにより、従来の窯業製品製造方法をそ
のまま用いて色々な窯業製品ができる。
[0006] The composition of slag varies depending on the location where municipal solid waste is generated, but it is within a certain range and is similar to the glaze of ceramics, so it can be used in the same manner as conventional ceramic raw materials, either alone or in the past. Various ceramic products can be produced by using the conventional ceramic product manufacturing method as it is, by combining with the ceramic raw materials of, and setting various temperatures.

【0007】[0007]

【実施例】例1 都市ごみ焼却灰を1450°Cに加熱
して熔融したのち冷却して得られたスラグを微粉砕し、
これにベントナイトを5〜10%添加して水分6%に調
整し、これを600mm×600mm×10mmの大き
さにプレス成型し、乾燥後1000°Cで焼成すること
により、クリーム色に着色された収縮及び吸水の少ない
陶板ができた。
EXAMPLES Example 1 Municipal solid waste incineration ash was heated to 1450 ° C., melted and then cooled, and the obtained slag was finely pulverized,
Bentonite was added to this in an amount of 5 to 10% to adjust the water content to 6%, press-molded into a size of 600 mm x 600 mm x 10 mm, dried and baked at 1000 ° C to give a cream color. A ceramic board with little shrinkage and water absorption was created.

【0008】例2 都市ごみ焼却灰70%と下水道汚泥
30%を混合して加熱熔融後冷却し、微粉砕したスラグ
70%と山砂利の水ひ粘土30%を水分20%で混練
後、土練機で押し出し、プレス成型後900°Cで焼成
することにより、茶色に着色された吸水率3%の瓦素地
が得られた。これに施釉またはいぶしをかけることによ
り、施釉瓦またはいぶし瓦となつた。
Example 2 70% of municipal waste incinerated ash and 30% of sewer sludge were mixed, heated and melted, then cooled, and finely ground 70% of slag and 30% of gravel suihi clay were mixed with water of 20%, and then soil. By extruding with a kneader, press-molding, and baking at 900 ° C., a roof tile substrate colored in brown and having a water absorption rate of 3% was obtained. Glazed tiles or smoked tiles were obtained by applying glaze or smoked to them.

【0009】例3 都市ごみ焼却灰90%と下水道汚泥
10%を同時熔融して冷却後微粉砕したスラグ60%と
相模地方の洗い砂粘土40%を混合し、水分23%にし
て押出成型機で幅300mm,厚さ20mm、長さ10
00mmの板に成型し、乾燥後ローラーハースキルンに
て1100°Cで焼成すると、チヨコレート色に着色さ
れた焼成収縮がなく、しかも、吸水性がほとんどないサ
イジング陶板ができた。
Example 3 90% of municipal waste incineration ash and 10% of sewer sludge were melted at the same time, 60% of slag finely ground after cooling, and 40% of washing sand clay of Sagami region were mixed to make water content 23%, and an extruder was used. Width 300 mm, thickness 20 mm, length 10
When it was molded into a 00 mm plate, dried and baked at 1100 ° C. in a roller hearth kiln, a sizing ceramic plate colored with a chicorylate color without shrinkage and having almost no water absorption was formed.

【0010】例4 都市ごみ焼却灰90%とガラス、陶
磁器、コンクリート等の不燃都市ごみの粉砕物10%を
混合して熔融し、徐冷して得られたスラグを粗粉砕し、
これを粒径2mm以下にふるい分ける。これを70%と
酸化鉄10%、頁岩粘土20%を少量の水ガラスとで水
分8%に調整し、これをレンガプレスにてレンガを乾式
成型する。乾燥後、800°Cで焼成することにより、
収縮及び吸水性のない黒色に着色された表面が粗面な味
わいのあるレンガが得られた。
Example 4 90% of municipal waste incinerated ash and 10% of crushed material of non-combustible municipal waste such as glass, ceramics, concrete, etc. were mixed and melted, and the slag obtained by slow cooling was roughly crushed,
This is screened to a particle size of 2 mm or less. 70%, iron oxide 10%, and shale clay 20% are adjusted to have a water content of 8% with a small amount of water glass, and bricks are dry-molded with a brick press. After drying, baking at 800 ° C
A tasteful brick with a black surface and no shrinkage or water absorption and a rough surface was obtained.

【0011】例5 都市ごみ焼却灰にクロムメツキスラ
ツジ10%を同時熔融したスラグを用いて例1の方法で
作つた製品は茶色の浮き上がつた渋い色の陶板となつ
た。
Example 5 The product produced by the method of Example 1 using the slag obtained by simultaneously melting 10% of chrome smelting sludge in municipal waste incineration ash turned into a dark-colored porcelain plate with a brown raised surface.

【0012】例6 都市ごみ焼却灰を熔融し、冷却した
スラグを粗粉砕して粒径5mm以下にふるい分けた。こ
のスラグを70%とセメント15%、頁岩粘土10%、
水ガラス5%を混合して水分30%に調整し、これを3
00mm×300mm×60mmの型の中に流し込んで
成型し、乾燥後1050°Cで焼成することにより耐摩
耗性に優れた黄味のある粗面の舗石ブロツクが得られ
た。
Example 6 Municipal refuse incineration ash was melted, and cooled slag was coarsely crushed and sieved to a particle size of 5 mm or less. 70% of this slag, 15% of cement, 10% of shale clay,
Mix 5% water glass to adjust the water content to 30% and add 3
By casting into a mold of 00 mm × 300 mm × 60 mm, molding, and drying and baking at 1050 ° C., a yellowish rough pavement block having excellent wear resistance was obtained.

【0013】例7 都市ごみ焼却灰を熔融し、冷却した
のち微粉砕したスラグ60%と石灰石採掘時に発生する
粘土30%とセリサイト質陶石10%を混合し、これを
水分18%に調整して真空土練機で押し出し成型し、乾
燥後、900°Cで焼成することにより灰茶色で吸水率
3%の陶管が得られた。
Example 7 Municipal refuse incineration ash was melted, cooled and then finely ground 60% slag, 30% clay generated during limestone mining, and 10% sericite porcelain stone were mixed to adjust the water content to 18%. Then, it was extrusion molded with a vacuum clay kneader, dried, and baked at 900 ° C. to obtain a porcelain tube with a grayish brown color and a water absorption rate of 3%.

【0014】例8 都市ごみ焼却灰50%と下水道汚泥
50%を混合して熔融し、冷却したスラグ74%とナト
リウムベントナイト5%、炭化珪素1%の混合物に水を
加えて湿式粉砕し、できた泥漿にセメント20%を加え
て脱水成型機で任意の大きさに成型した。これを乾燥後
1100°Cで焼成すると嵩比重0.5に発泡した焼成
品ができた。これを任意の大きさに切断することにより
軽量断熱材が得られた。
Example 8 50% of municipal waste incineration ash and 50% of sewer sludge were mixed and melted, and water was added to a cooled mixture of 74% of slag, 5% of sodium bentonite and 1% of silicon carbide, and wet grinding was performed. 20% cement was added to the sludge and molded into an arbitrary size with a dehydration molding machine. When this was dried and calcined at 1100 ° C, a calcined product foamed to a bulk specific gravity of 0.5 was obtained. A lightweight heat insulating material was obtained by cutting this into an arbitrary size.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C04B 35/00 C04B 35/00 V (56)参考文献 特開 昭53−88657(JP,A) 特開 平2−261587(JP,A) 福本勤著「廃棄物処理工学」(1980−7 −1)(株)朝倉書店P.162〜171─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location C04B 35/00 C04B 35/00 V (56) References JP-A-53-88657 (JP, A) JP-A-2-261587 (JP, A) Tsutomu Fukumoto "Waste treatment engineering" (1980-7-1) Asakura Shoten Co., Ltd. 162 ~ 171

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 都市ごみ焼却灰を熔融するまで加熱し、
冷却して得られたスラグを適当な粒径に粉砕することに
より窯業原料化することを特徴とする都市ごみ焼却灰を
利用した窯業原料の製造方法。
1. The municipal waste incineration ash is heated until it is melted,
To crush the slag obtained by cooling to an appropriate particle size
A method for manufacturing a ceramic raw material using municipal waste incineration ash, which is characterized by making it a more ceramic raw material .
【請求項2】 都市ごみ焼却灰に下水道汚泥等の廃棄物
を混合して熔融することを特徴とする請求項1記載の都
市ごみ焼却灰を利用した窯業原料の製造方法。
2. The method for producing a ceramic raw material using municipal waste incineration ash according to claim 1, wherein waste materials such as sewer sludge are mixed with the municipal waste incineration ash and melted.
【請求項3】 請求項1または請求項2記載の窯業原料
の製造方法において得られた窯業原料と窯業原料成分調
整材とを水とともに混合混練して製品形状に成型し、成
型品を乾燥後に800℃〜1100℃で焼成することに
より焼成品を製造することを特徴とする焼成品の製造方
法。
3. The ceramic raw material according to claim 1 or 2.
Ceramic raw materials obtained by the manufacturing method of
The material is mixed with water and kneaded to form the product shape.
After baking the mold, baking at 800 ℃ ~ 1100 ℃
A method for manufacturing a fired product, which is characterized by producing a more fired product.
Law.
JP3259673A 1991-09-10 1991-09-10 Manufacturing method of ceramic raw materials and manufacturing method of fired products using incinerated ash of municipal waste Expired - Lifetime JPH0829313B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3259673A JPH0829313B2 (en) 1991-09-10 1991-09-10 Manufacturing method of ceramic raw materials and manufacturing method of fired products using incinerated ash of municipal waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3259673A JPH0829313B2 (en) 1991-09-10 1991-09-10 Manufacturing method of ceramic raw materials and manufacturing method of fired products using incinerated ash of municipal waste

Publications (2)

Publication Number Publication Date
JPH0568959A JPH0568959A (en) 1993-03-23
JPH0829313B2 true JPH0829313B2 (en) 1996-03-27

Family

ID=17337316

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3259673A Expired - Lifetime JPH0829313B2 (en) 1991-09-10 1991-09-10 Manufacturing method of ceramic raw materials and manufacturing method of fired products using incinerated ash of municipal waste

Country Status (1)

Country Link
JP (1) JPH0829313B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2592041B2 (en) * 1993-10-01 1997-03-19 株式会社テトラ Concrete block using garbage waste
TW201215586A (en) * 2010-10-05 2012-04-16 Qi-Chang Lv Method of preparing glaze using sludge of head-water point and ceramic product made of the glaze
CN111704446B (en) * 2020-06-03 2022-08-05 蒙娜丽莎集团股份有限公司 Sodium-based bentonite type foamed ceramic blank, sodium-based bentonite type foamed ceramic tile and preparation method thereof

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5388657A (en) * 1977-01-14 1978-08-04 Ebara Infilco Co Ltd Treating method for incineration ash
JPH02261587A (en) * 1989-03-31 1990-10-24 Katsumi Takao Device for vitrifying waste incineration ash

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
福本勤著「廃棄物処理工学」(1980−7−1)(株)朝倉書店P.162〜171

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