JP2002293659A - Method of manufacturing porous ceramic by using waste building material containing asbestos and incineration ash of sewage sludge - Google Patents

Method of manufacturing porous ceramic by using waste building material containing asbestos and incineration ash of sewage sludge

Info

Publication number
JP2002293659A
JP2002293659A JP2001095168A JP2001095168A JP2002293659A JP 2002293659 A JP2002293659 A JP 2002293659A JP 2001095168 A JP2001095168 A JP 2001095168A JP 2001095168 A JP2001095168 A JP 2001095168A JP 2002293659 A JP2002293659 A JP 2002293659A
Authority
JP
Japan
Prior art keywords
asbestos
sewage sludge
incineration ash
building material
porous 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
Application number
JP2001095168A
Other languages
Japanese (ja)
Inventor
Takashi Ishikawa
堯 石川
Ryuichi Takahashi
隆一 高橋
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.)
IG Technical Research Inc
Original Assignee
IG Technical Research Inc
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 IG Technical Research Inc filed Critical IG Technical Research Inc
Priority to JP2001095168A priority Critical patent/JP2002293659A/en
Priority to US09/878,317 priority patent/US20020027316A1/en
Publication of JP2002293659A publication Critical patent/JP2002293659A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To solve the problem that asbestos-containing building materials and incineration ash of sewage sludge are left as they are since there is no effective treatment method or they are buried under the ground for reclamation. SOLUTION: Asbestos-absent porous ceramic to be reused is manufactured by mixing the waste of asbestos-containing building materials, incineration ash of sewage sludge, aggregate and the like and firing the mixture.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明はアスベストを含有する建
材の廃棄物と埋め立て処理されていた下水汚泥焼却灰と
を焼成させることにより、アスベストを不在化して再利
用したリサイクル率の高い透水ブロックなどの多孔質セ
ラミックを得る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 highly recyclable water-permeable block made by asbestos-absent and reused by burning asbestos-containing building material waste and landfill-treated sewage sludge incineration ash. And a method for producing a porous ceramic.

【0002】[0002]

【従来の技術】クリソタイルを代表とした健康に有害で
あるといわれるアスベストを含有する建材は30年以上
に亘り、住宅及び非住宅の建物の屋根材や壁材として多
く使われている。近年はアスベスト含有量を少なくした
建材も上市されつつあるが、それでも含有量はゼロでは
なく、また過去に使用された含有量の多い建材は依然と
して住宅等に使用されたままであり、当然ながら、その
劣化に伴ってアスベストに拘わる問題が発生し、特にそ
の廃棄物については有効な処理法が未だ確立されてはい
ない。
2. Description of the Related Art Asbestos-containing building materials, which are said to be harmful to health, such as chrysotile, have been used as roofing materials and wall materials for residential and non-residential buildings for more than 30 years. In recent years, building materials with reduced asbestos content are also being marketed, but the content is still not zero, and building materials with a high content used in the past are still used in houses and so on. Deterioration has caused problems related to asbestos, and no effective disposal method has been established for wastes in particular.

【0003】例えば、アスベスト建材の廃棄物処理方法
としては、大きな塊のままで土中に埋設する、または高
温で熔融固化させ安定型の最終処分場に埋め立てる、等
の処理が行われている。
For example, as a method for treating asbestos building material waste, a process of burying it in soil as a large lump or melting and solidifying it at a high temperature and burying it in a stable final disposal site is performed.

【0004】一方で、下水汚泥焼却灰は殆どが埋め立て
処理されており、土管やタイル等の原料の一部として利
用、または軽量骨材として各種製品に利用する等の再利
用化が研究されてはいるが、まだ実用化には至らない
等、有効な再利用はなされていない。
On the other hand, sewage sludge incineration ash is mostly landfilled, and its reuse as a part of raw materials such as clay pipes and tiles or as a lightweight aggregate for various products has been studied. However, it has not yet been put to practical use and has not been effectively reused.

【0005】[0005]

【発明が解決しようとする課題】したがって、アスベス
トを含む建材や下水汚泥焼却灰は有効な処理方法がない
ままに放置され、または埋め立て処理されている。
Accordingly, asbestos-containing building materials and sewage sludge incineration ash have been left without any effective treatment method or landfilled.

【0006】[0006]

【課題を解決するための手段】アスベスト含有建材の廃
棄物と下水汚泥焼却灰と成形バインダと骨材等とを混合
し、焼成させることにより、アスベストを不在化させた
多孔質セラミックとして再利用するための製造方法を提
供する。
The waste of asbestos-containing building material, sewage sludge incineration ash, forming binder, aggregate, and the like are mixed and fired to reuse asbestos-free porous ceramic. To provide a manufacturing method.

【0007】[0007]

【発明の実施の形態】本発明で用いるアスベスト含有建
材は、アスベストを混入したセメント硬化物及びアスベ
ストを混入したけい酸カルシウム等の硬化物である。例
えば、平型彩色スレート、波型スレート、スレート、石
綿けい酸カルシウム板、スラグせっこう板、押出成型セ
メント板、窯業系サイディングなどである。また、これ
らは主に取り替えや建て替えに伴って発生するアスベス
ト含有の屋根材や壁材の廃棄物を前提にしているが、当
然、使用されずに廃棄されるものも含まれる。
BEST MODE FOR CARRYING OUT THE INVENTION The asbestos-containing building material used in the present invention is a hardened material such as cement hardened with asbestos and a hardened material such as calcium silicate mixed with asbestos. For example, flat colored slate, corrugated slate, slate, calcium asbestos silicate board, slag gypsum board, extruded cement board, ceramic siding, etc. In addition, although these are premised on waste of asbestos-containing roofing materials and wall materials mainly generated by replacement or rebuilding, naturally, waste materials are discarded without being used.

【0008】取り替えや建て替えに伴って発生するアス
ベスト含有建材は既に劣化しているので、アスベストを
飛散しやすくなっており、回収、運搬や保管等には特に
注意する必要がある。
Since the asbestos-containing building material generated by replacement or rebuilding has already deteriorated, asbestos is liable to be scattered, and special attention must be paid to collection, transportation and storage.

【0009】アスベスト含有建材の廃棄物を必要に応じ
て破砕、粉砕する。破砕、粉砕方法としてはいろいろあ
るが、適宜、必要に応じて選択すればよい。
[0009] Asbestos-containing building material waste is crushed and pulverized as necessary. There are various crushing and pulverizing methods, and they may be appropriately selected as needed.

【0010】本発明で用いる下水汚泥焼却灰の主成分
は、Si、Al、Fe、Ca、P、Mg、Na、Kであ
り、P、Ca、Na、Kといった容易にガラス相を生成
する成分が多く含まれており、比較的低温で反応と焼成
が同時に進むものである。
[0010] The main components of the sewage sludge incineration ash used in the present invention are Si, Al, Fe, Ca, P, Mg, Na, and K, such as P, Ca, Na, and K, which easily form a glass phase. , And the reaction and firing proceed simultaneously at a relatively low temperature.

【0011】本発明で用いる成形バインダは、例えば粘
土、ベントナイト、有機質糊等の一つ又は複数を組み合
わせたものであり、プレス等により容易に成形可能とす
るものである。また、水ガラスを使用することもできる
が、水ガラスの場合は二酸化炭素ガスを吹付けて硬化さ
せる。
The molding binder used in the present invention is, for example, one or a combination of clay, bentonite, organic glue and the like, and can be easily molded by pressing or the like. Water glass can also be used, but in the case of water glass, it is cured by blowing carbon dioxide gas.

【0012】本発明で用いる骨材は耐火度の高い無機材
で、例えばセルベン(タイル廃材、陶磁器廃材等)、石
材クズ、ケイ砂、フライアッシュ、シャモット、キラ、
鉱滓等の一つ又は複数を組み合わせたものである。
The aggregate used in the present invention is an inorganic material having a high fire resistance, such as seruben (waste of tiles, waste of ceramics, etc.), stone waste, silica sand, fly ash, chamotte, killer,
It is a combination of one or more of slag and the like.

【0013】また、アスベスト含有建材廃棄物と下水汚
泥焼却灰とは主に溶融バインダとして機能するが、該焼
成物の混合量を増やせば多孔質セラミックとするための
焼成温度を高くする必要があり、燃料コストの上昇は避
けられないが、溶融助剤を添加することにより、より低
い焼成温度とすることができる。
Further, asbestos-containing building material waste and sewage sludge incineration ash mainly function as a molten binder. However, if the mixing amount of the fired material is increased, it is necessary to raise the firing temperature for forming a porous ceramic. Although an increase in fuel cost cannot be avoided, a lower firing temperature can be achieved by adding a melting aid.

【0014】溶融助剤は、フリット、釉薬汚泥、ガラス
廃材等の一つ又は複数を組み合わせたものである。
The melting aid is a combination of one or more of frit, glaze sludge, glass waste, and the like.

【0015】上記のものを焼成させるには600℃以上
とする。これは、600℃以上で焼成するとX線回折に
よりアスベストのピークが不在となるからである。
In order to fire the above, the temperature is set to 600 ° C. or higher. This is because the asbestos peak is absent by X-ray diffraction when firing at 600 ° C. or higher.

【0016】焼成に要する時間は特に限定しないが、上
記焼成温度で建材廃棄物に含まれるアスベストがX線回
折により不在となり、さらに溶融バインダが該焼成温度
で溶融し、バインダとして機能するまでの時間があれば
よい、それらは混合される溶融バインダの成分、粒子
径、さらに成形体の大きさ、窯の条件等で決定されるも
のである。焼成の方法としては、例えばトンネルキルン
やローラハウスキルンがある。
The time required for firing is not particularly limited, but asbestos contained in building material waste is absent due to X-ray diffraction at the above firing temperature, and the time required for the molten binder to melt at the firing temperature and function as a binder. These are determined by the components of the molten binder to be mixed, the particle size, the size of the molded body, the conditions of the kiln, and the like. Examples of the firing method include a tunnel kiln and a roller house kiln.

【0017】アスベスト含有建材廃棄物を仮焼成してか
ら下水汚泥焼却灰や骨材等と混合、焼成する場合に較べ
て、仮焼成しないで混合、焼成する場合では収縮率が大
きくなる。これは、空隙率を大きくすることであり、よ
り多孔質としての性能を発揮することになる。
Compared with the case where the asbestos-containing building material waste is pre-fired and then mixed and fired with sewage sludge incineration ash or aggregate, the shrinkage rate is increased when mixing and firing without pre-firing. This means that the porosity is increased, and the performance as a more porous material is exhibited.

【0018】多孔質セラミックの化粧方法としては、そ
のまま、混合時に釉薬又は顔料を加えて焼成する、焼成
後に釉薬をかけてさらに焼成する、別に化粧層を設けた
多孔質セラミックと一体化する等の方法がある。
As a cosmetic method of the porous ceramic, a glaze or a pigment is added at the time of mixing as it is, and the mixture is baked. There is a way.

【0019】以下に、実施例を示して具体的に説明する
が、本発明はこれらの実施例により限定されるわけでは
ない。
Hereinafter, the present invention will be described specifically with reference to Examples, but the present invention is not limited to these Examples.

【0020】(実施例1)アスベスト含有建材廃棄物
(商品名コロニアル:表1に主な組成を示す)をジョー
クラッシャーで10ミリ以下に破砕し、次にボールミル
に入れ、水を加えながら約5時間粉砕し、得られた泥漿
を乾燥して、乾燥粉を得た。使用した下水汚泥焼却灰の
組成比を表2に示す。溶融助剤としてFerro社の
「MX−3P」を、成型バインダとして粘土(乾燥品、
80メッシュ通過)を、そして骨材としてセルベン(7
〜20メッシュ)を使用した。表3に示した混合比率で
混合し、水分を適宜添加しながら混練造粒し、プレス機
で平板(50g/枚)に造形し、電気炉で1050℃、
1時間焼成した。得られた板材の物性値は表4のとおり
であり、多孔質セラミックの一例である透水ブロックの
評価としては優れたものであることがわかった。また、
この焼成物はX線回折によりアスベストのピークを示さ
ないことが確認された。
Example 1 Asbestos-containing building material waste (colonial (trade name), whose main composition is shown in Table 1) was crushed with a jaw crusher to 10 mm or less, then put into a ball mill and added with water for about 5 mm. The mixture was pulverized for an hour, and the obtained slurry was dried to obtain a dried powder. Table 2 shows the composition ratio of the used sewage sludge incineration ash. "MX-3P" manufactured by Ferro as a melting aid and clay (dried product,
80 mesh) and Cerven (7
2020 mesh). The mixture was mixed at the mixing ratios shown in Table 3, kneaded and granulated while appropriately adding water, formed into a flat plate (50 g / sheet) by a press machine, and heated at 1050 ° C. in an electric furnace.
It was baked for 1 hour. The physical properties of the obtained plate material are as shown in Table 4, and it was found that the evaluation of the water-permeable block as an example of the porous ceramic was excellent. Also,
It was confirmed that the fired product did not show an asbestos peak by X-ray diffraction.

【表1】 [Table 1]

【表2】 [Table 2]

【表3】 [Table 3]

【表4】 [Table 4]

【0021】[0021]

【発明の効果】本発明の製造方法によれば、健康に有
害であるとといわれるアスベストの廃棄物を不在化した
多孔質セラミックとして再利用できる、埋め立て処理
されていた下水汚泥焼却灰、さらにセルベンやガラス廃
材とも混合、反応、焼成させることができ、リサイクル
率が高くアスベストを不在化した多孔質セラミックとし
て再利用できる、アスベスト含有建材廃棄物の混合率
を増やせば、焼成温度を高くする必要があるが、溶融助
剤を添加することで焼成温度を低くでき、燃料コスト等
が低減される、等の特徴、効果が得られる。
According to the production method of the present invention, landfill-treated sewage sludge incineration ash, which can be reused as a porous ceramic in which asbestos waste which is said to be harmful to health is absent, Can be mixed, reacted, and fired with glass waste material, and can be reused as a porous ceramic with a high recycling rate and no asbestos.If the mixing rate of asbestos-containing building material waste is increased, the firing temperature must be increased. However, by adding a melting aid, the sintering temperature can be lowered, and the characteristics and effects such as the reduction of fuel cost can be obtained.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 主にアスベスト含有建材廃棄物と下水汚
泥焼却灰とを焼成したことを特徴とする多孔質セラミッ
クの製造方法。
1. A method for producing a porous ceramic, comprising mainly burning asbestos-containing building material waste and sewage sludge incineration ash.
JP2001095168A 2000-06-14 2001-03-29 Method of manufacturing porous ceramic by using waste building material containing asbestos and incineration ash of sewage sludge Pending JP2002293659A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP2001095168A JP2002293659A (en) 2001-03-29 2001-03-29 Method of manufacturing porous ceramic by using waste building material containing asbestos and incineration ash of sewage sludge
US09/878,317 US20020027316A1 (en) 2000-06-14 2001-06-12 Asbestos-free product sintered from building material wastes containing asbestos and method of producing the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001095168A JP2002293659A (en) 2001-03-29 2001-03-29 Method of manufacturing porous ceramic by using waste building material containing asbestos and incineration ash of sewage sludge

Publications (1)

Publication Number Publication Date
JP2002293659A true JP2002293659A (en) 2002-10-09

Family

ID=18949259

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001095168A Pending JP2002293659A (en) 2000-06-14 2001-03-29 Method of manufacturing porous ceramic by using waste building material containing asbestos and incineration ash of sewage sludge

Country Status (1)

Country Link
JP (1) JP2002293659A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009005081A1 (en) * 2007-07-02 2009-01-08 Nihon Yamamura Glass Co., Ltd. Method of asbestos vitrification
JP2011031183A (en) * 2009-08-03 2011-02-17 Toru Kubota Method of manufacturing refractory brick from detoxified substance of asbestos as raw material

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001353479A (en) * 2000-06-14 2001-12-25 Ig Tech Res Inc Sintered body by safening reaction of building waste material containing asbestos

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001353479A (en) * 2000-06-14 2001-12-25 Ig Tech Res Inc Sintered body by safening reaction of building waste material containing asbestos

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009005081A1 (en) * 2007-07-02 2009-01-08 Nihon Yamamura Glass Co., Ltd. Method of asbestos vitrification
JPWO2009005081A1 (en) * 2007-07-02 2010-08-26 日本山村硝子株式会社 Vitrification method of asbestos
JP2011031183A (en) * 2009-08-03 2011-02-17 Toru Kubota Method of manufacturing refractory brick from detoxified substance of asbestos as raw material

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