JPH07112174A - Production of artificial sand - Google Patents

Production of artificial sand

Info

Publication number
JPH07112174A
JPH07112174A JP28789491A JP28789491A JPH07112174A JP H07112174 A JPH07112174 A JP H07112174A JP 28789491 A JP28789491 A JP 28789491A JP 28789491 A JP28789491 A JP 28789491A JP H07112174 A JPH07112174 A JP H07112174A
Authority
JP
Japan
Prior art keywords
ashes
sludge incineration
water
artificial sand
pellets
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.)
Granted
Application number
JP28789491A
Other languages
Japanese (ja)
Other versions
JP2582493B2 (en
Inventor
Hiroki Honda
裕姫 本多
Satoshi Okuno
敏 奥野
Shuichi Chida
修一 地田
Toshio Tsuru
俊雄 津留
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP28789491A priority Critical patent/JP2582493B2/en
Publication of JPH07112174A publication Critical patent/JPH07112174A/en
Application granted granted Critical
Publication of JP2582493B2 publication Critical patent/JP2582493B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To provide a technique for forming resources at a low cost to stably utilize a large amt. of sewer sludge incineration ashes by adding water to the sewer sludge incineration ashes, mixing and kneading these ashes to form a mixture, pelletizing this mixture, calcining the pellets after drying and crushing the calcined pellets after cooling, thereby producing artificial sand. CONSTITUTION:Only water is added at a prescribed mixing ratio to the sewer sludge incineration ashes and after the ashes are sufficiently kneaded by a kneading machine 1, the mixture is pelletized or molded to a plate form of prescribed sizes by a molding machine 2. The moldings are dried by a dry calcination furnace 3 and are then calcined at a prescribed temp. (m. p. or below). The calcined pellets are allowed to stand for natural cooling or allowed to cool down to the prescribed temp., and thereafter, the pellets are cooled with water and are crushed by a crushing machine 4. The crushed ashes are classified by a classifying machine 5 and are subjected to grain size adjustment according to applications thereof by which the artificial sand is produced. Consequently, the technique for using resources at the low cost to stably utilize a large amt. of the sewer sludge incineration ashes is obtd.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は下水汚泥処理設備で発生
する下水汚泥焼却灰から人工砂を製造する方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for producing artificial sand from sewage sludge incineration ash generated in sewage sludge treatment equipment.

【0002】[0002]

【従来の技術】従来、下水汚泥焼却灰は、加湿後、埋立
処分するか、セメント或いは石灰等と混合し造粒固化し
て埋立処分していた。また、最近では、溶融スラブ化し
て埋立処分したり、加圧成形し焼成レンガを作ったりし
ている。
2. Description of the Related Art Conventionally, sewage sludge incineration ash has been humidified and then landfilled, or it has been mixed with cement, lime or the like, granulated and solidified, and then landfilled. In addition, recently, molten slabs have been used for landfill disposal, or pressure-molded to make fired bricks.

【0003】[0003]

【発明が解決しようとする課題】前述の従来技術には次
のような問題点がある。埋立処分する場合には、埋立処
分地の確保が困難であり、更に自然環境保護及び汚泥処
分費の高騰等の問題がある。また焼成レンガ等を製造す
る場合には、処理コスト、品質、販路等の対策が不充分
である。
The above-mentioned prior art has the following problems. When landfilling, it is difficult to secure landfill sites, and there are problems such as protection of the natural environment and soaring sludge disposal costs. In addition, when manufacturing fired bricks and the like, measures such as treatment cost, quality and sales channels are insufficient.

【0004】本発明は、下水汚泥焼却灰を大量に安定的
に利用するコストの低廉な資源化技術を提供することを
目的とするものである。
It is an object of the present invention to provide a resource-saving technique for stably utilizing a large amount of sewage sludge incineration ash at a low cost.

【0005】[0005]

【課題を解決するための手段】下水汚泥焼却灰に、所定
混合比で水のみを添加し、十分に混練後、所定寸法に造
粒又は板状成型し、乾燥した後、所定温度(融点以下)
にて焼成する。次に、この焼成物を自然放冷又は、所定
温度まで自然放冷、その後水冷して、破砕、分級により
使途に応じた粒度調整を行ない、人工砂を製造する。ま
た、微細物は、焼却灰側へ戻し、再度原料として使用す
る。
[Means for Solving the Problems] To a sewage sludge incineration ash, only water is added at a predetermined mixing ratio, and after sufficiently kneading, granulated or plate-shaped to a predetermined size and dried, and then a predetermined temperature (below the melting point) )
Bake at. Next, the calcined product is naturally cooled or naturally cooled to a predetermined temperature, and then water cooled, and crushed and classified to adjust the particle size according to the purpose of use to produce artificial sand. In addition, the fine material is returned to the incineration ash side and used again as a raw material.

【0006】[0006]

【作用】流動層炉で焼却処理した下水汚泥焼却灰は、脱
水ケーキの種類(高分子系又は石灰系)に拘らず、その
粒度は数十ミクロン以下と非常に微細である。そして、
この灰に適量の水を添加し、十分に混練することによ
り、造粒等の成形が可能となる。そこで、所定大の粒状
物又は板状物に成形し、予備乾燥後、焼成炉内で100
0〜1200℃の焼成温度にて、10〜30分間焼成す
る。その後、自然放冷又は、500℃以下は水冷する。
そして、これを破砕分級し、粒度調整することにより、
天然砂に匹敵する物性を有する人工砂を製造することが
できる。これは、焼成時に均一加熱されて、材料内部ま
で均一焼成化が達成されたことに依るもので、これには
前処理である材料の成形条件(形状、寸法、含水率他)
が大きく関与している。
The sewage sludge incineration ash incinerated in the fluidized bed furnace has a very fine particle size of several tens of microns or less, regardless of the type of dehydrated cake (polymer type or lime type). And
By adding an appropriate amount of water to this ash and sufficiently kneading, it becomes possible to perform molding such as granulation. Therefore, it is formed into a granular or plate-like material of a predetermined size, pre-dried, and then 100
Baking is carried out for 10 to 30 minutes at a baking temperature of 0 to 1200 ° C. Then, it is naturally cooled or water-cooled at 500 ° C or lower.
And by crushing and classifying this and adjusting the particle size,
It is possible to manufacture artificial sand having physical properties comparable to natural sand. This is due to the fact that the material was uniformly heated during firing to achieve uniform firing inside the material. This is a pretreatment of the material molding conditions (shape, dimensions, water content, etc.).
Is heavily involved.

【0007】即ち、焼成前の寸法、形状、含水率及び加
熱条件が適切でない場合には、焼成工程にてヒビ割れた
り、均一焼成ができず、焼成物の内部と外部で焼成度の
異なる性状となる。
That is, if the size, shape, water content and heating conditions before firing are not appropriate, cracks may occur in the firing process or uniform firing may not be possible, resulting in different firing degrees inside and outside the fired product. Becomes

【0008】[0008]

【実施例】本発明による下水汚泥焼却灰からの人工砂製
造方法のブロックフロー線図を図1に示す。本図に示す
様に、焼却灰はホッパ等から定量的に混練機1へ供給さ
れ、ここで、所定量(重量比で15〜30%)の水と混
合、混練し、次工程の成形機2へ送られる。尚、造粒す
るために必要な水添加量は、焼却灰の粒径と密接な関係
があり、微粒子程、少量の水添加にて保形力が発生し、
下水汚泥の流動層焼却灰の場合、適当な水添加量は15
〜30%であった。
EXAMPLE A block flow diagram of the method for producing artificial sand from sewage sludge incineration ash according to the present invention is shown in FIG. As shown in the figure, the incinerated ash is quantitatively supplied from a hopper or the like to the kneading machine 1, where it is mixed and kneaded with a predetermined amount (15 to 30% by weight) of water, and the molding machine of the next step. Sent to 2. The amount of water added for granulation is closely related to the particle size of incinerated ash, and the finer the particles, the smaller the amount of water added to the shape-retaining power,
For fluidized bed incineration ash of sewage sludge, the appropriate amount of water added is 15
Was 30%.

【0009】次に、成形機2では、最大径10mmφの
粒状、か又は厚さ10mm以下の板状に成形され、板状
物は約数十mm大に砕いて乾燥焼成炉3へ導かれる。こ
こでは、添加水分の乾燥に引き続き、焼結反応が進行
し、所定温度にて、10〜30分間で焼成が終了する。
この所定温度は、対象物の成分構成により異なり、融点
よりやや低い1000〜1200℃の範囲である。
Next, in the molding machine 2, it is formed into a granular shape having a maximum diameter of 10 mmφ or a plate shape having a thickness of 10 mm or less, and the plate-like material is crushed to a size of about several tens of mm and introduced into the drying and firing furnace 3. Here, the sintering reaction proceeds after the drying of the added water, and the firing is completed at a predetermined temperature for 10 to 30 minutes.
This predetermined temperature varies depending on the component composition of the object and is in the range of 1000 to 1200 ° C., which is slightly lower than the melting point.

【0010】また、焼成品の収縮率即ち、気孔率の大小
は、昇温速度、焼成時の残留水分、焼成温度に影響さ
れ、一方、製品強度は図2に示す様に処理温度に大きく
影響される。図中、A域は固相焼結の段階で、焼結状態
は未だ不十分で、B域は、粒子内部に僅かに液相が生成
して若干焼結が進行し、C域は、液相が生成することに
より、完全に液相焼結し、粒子同士が十分に固着し、D
域では、更に液相が増加し、粒子同士が合体し始め、E
域では、内部より脱ガス(例えば、CO2 ,SO 2 他)
によるバブリングを起し、発泡するためここでの製品強
度は極端に低下することになる。また、更に昇温する
と、全体が溶融スラグ化し、徐冷結晶化することにより
強度は向上する。そして、最適焼結温度として同図中、
C域が選ばれる。しかし、このC域は、材料組成にも依
るが、一般に下水汚泥焼却灰の場合、数十℃と非常に狭
い範囲となっている。そこで、材料の内外部とも均一な
焼結状態を達成するためには、焼成炉温の制御以外に、
被処理物内の温度分布を前記のC域の温度範囲内に納め
る事が重要となってくる。
Further, the shrinkage rate of the baked product, that is, the porosity is large or small.
Influences the heating rate, residual water content during firing, and firing temperature.
On the other hand, the product strength is large at the processing temperature as shown in Fig.2.
To be affected. In the figure, region A is in the state of sintering at the stage of solid phase sintering.
Is still insufficient, and a slight liquid phase is generated inside the particles in the B region.
Then, sintering proceeds a little, and in the C region, a liquid phase is generated.
More, complete liquid phase sintering, particles are firmly fixed to each other, D
In the region, the liquid phase further increases, particles begin to coalesce, and
In the area, degassing from inside (for example, CO2, SO 2other)
Bubbling and foaming due to product strength here
The degree will be extremely low. Moreover, the temperature is further raised.
And the whole becomes molten slag, and by gradually cooling and crystallization
Strength is improved. And as the optimum sintering temperature in the figure,
Area C is selected. However, this C region also depends on the material composition.
However, in the case of sewage sludge incineration ash, it is generally very narrow at several tens of degrees Celsius.
It is within the range. Therefore, both inside and outside of the material are uniform
In order to achieve a sintered state, in addition to controlling the firing furnace temperature,
Keep the temperature distribution in the object to be processed within the temperature range of the above C range.
Is important.

【0011】そこで、発明者らは、種々の基礎試験、伝
熱解析等を行ない、焼成前被処理物(水添加造粒物)の
最大厚さ又は径として10mmφ以下とすることによ
り、焼成時の被処理物内の温度分布を前記C域の温度範
囲内におさえ、均一な焼成物を得ることができた。つぎ
に、焼成固化物は、自然放冷(空冷)するか、又は、5
00℃まで自然放冷した後、水冷し、破砕機4に運ばれ
て、ここで製品として要求される粒径に破砕され、分級
機5で分級される。尚、この分級操作において、大径物
は再度破砕し、また微細物はプロセス入口側へ返送さ
れ、焼却灰と一緒に再度焼成処理される。
Therefore, the inventors conducted various basic tests, heat transfer analysis, etc., and set the maximum thickness or diameter of the pre-firing target material (water-added granulated material) to 10 mmφ or less, thereby It was possible to obtain a uniform calcined product by controlling the temperature distribution in the article to be treated within the temperature range of the C range. Next, the calcined solidified product is allowed to cool naturally (air cooling) or 5
After being naturally cooled to 00 ° C., it is cooled with water, conveyed to a crusher 4, where it is crushed to a particle size required as a product and classified by a classifier 5. In addition, in this classification operation, the large-sized product is crushed again, and the fine product is returned to the process inlet side and is again fired together with the incinerated ash.

【0012】本システムにて製造した人工砂の物理的性
状を第1表に、また、この人工砂の流動床焼却炉用流動
砂としての適用性評価結果を第2表に示す。これらよ
り、下水汚泥焼却灰に水添加し、造粒、焼成して製造し
た人工砂は、流動砂として従来使用している天然砂の代
替品として十分に使用可能であることが判明した。
The physical properties of the artificial sand produced by this system are shown in Table 1, and the applicability evaluation results of this artificial sand as fluidized sand for a fluidized bed incinerator are shown in Table 2. From these, it was found that the artificial sand produced by adding water to sewage sludge incineration ash, granulating and firing it can be sufficiently used as a substitute for natural sand that has been conventionally used as fluidized sand.

【0013】次の表1はこのようにして得られた人工砂
の物理的性状を示すものであり、表2は焼却炉用流動材
としての適用性評価試験結果例を示すものである。
The following Table 1 shows the physical properties of the artificial sand thus obtained, and Table 2 shows an example of the results of the applicability evaluation test as a fluid material for an incinerator.

【0014】[0014]

【表1】 [Table 1]

【0015】[0015]

【表2】 [Table 2]

【0016】[0016]

【発明の効果】本発明による人工砂の製造方法は、下水
汚泥焼却灰に水を添加し、混合、混練して混合物を作
り、この混合物を造粒成型して乾燥した後で焼成して焼
成物を作り、この焼成物を冷却後、破砕して人工砂を製
造することにより、次の効果を有する。
Industrial Applicability The method for producing artificial sand according to the present invention comprises adding water to sewage sludge incineration ash, mixing and kneading to make a mixture, granulating the mixture, drying and firing the mixture. The following effects can be obtained by producing a product, cooling the fired product, and then crushing the product to produce artificial sand.

【0017】従来、埋立処分が主流であった下水汚泥焼
却灰から天然流動砂の代替品としての人工流動砂を製造
することができる。また、焼却灰の発生源である下水処
理場内での再利用が可能であり、埋立焼却灰量の減量化
(埋立地の延命化)と省資源化に貢献することができ
る。更に、この人工砂を焼成レンガ等の骨材として使用
することにより、寸法精度の高い焼成レンガ製造システ
ムを提供できると共に、建設用資材としての活用により
広域的利用性も生ずる。
Conventionally, artificial fluidized sand as a substitute for natural fluidized sand can be produced from sewage sludge incineration ash, which has hitherto been mainly used for landfill disposal. In addition, it can be reused in the sewage treatment plant, which is the source of incineration ash, and can contribute to reduction of the amount of landfill incineration ash (prolonging the life of the landfill) and resource saving. Furthermore, by using this artificial sand as an aggregate for fired bricks, etc., a fired brick manufacturing system with high dimensional accuracy can be provided, and it can be used as a construction material for wide-area utilization.

【0018】以上により、従来の一過型の処理形態か
ら、資源循環型の処理方法を提供することができる。
As described above, it is possible to provide a resource recycling type processing method from the conventional transient type processing method.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の実施例のブロックフロー線図である。FIG. 1 is a block flow diagram of an embodiment of the present invention.

【図2】本発明の実施例における処理温度と製品強度の
関係を示す線図である。
FIG. 2 is a diagram showing a relationship between processing temperature and product strength in an example of the present invention.

【符号の説明】[Explanation of symbols]

1 混練機 2 成形機 3 乾燥焼成炉 4 破砕機 5 分級機 1 Kneader 2 Molding machine 3 Drying firing furnace 4 Crusher 5 Classifier

───────────────────────────────────────────────────── 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 18/10 Z (72)発明者 奥野 敏 神奈川県横浜市中区錦町12番地 三菱重工 業株式会社横浜製作所内 (72)発明者 地田 修一 埼玉県東松山市五領町12−71 (72)発明者 津留 俊雄 東京都府中市押立町5−14−46─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location C04B 18/10 Z (72) Inventor Satoshi Okuno 12 Nishiki-cho, Naka-ku, Yokohama-shi, Kanagawa Mitsubishi Heavy Industries Shares Company Yokohama Works (72) Inventor Shuichi Jida 12-71 Goryocho, Higashimatsuyama City, Saitama Prefecture (72) Inventor Toshio Tsuru 5-14-46, Oshidate Town, Fuchu City, Tokyo

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 下水汚泥焼却灰に水を添加し、混合、混
練して混合物を作り、この混合物を造粒成型して乾燥し
た後で焼成して焼成物を作り、この焼成物を冷却後、破
砕して人工砂を製造することを特徴とする人工砂の製造
方法。
1. Water is added to sewage sludge incineration ash, mixed and kneaded to form a mixture, and the mixture is granulated, dried, and fired to produce a fired product, which is then cooled. A method for producing artificial sand, which comprises crushing to produce artificial sand.
JP28789491A 1991-11-01 1991-11-01 Manufacturing method of artificial sand Expired - Lifetime JP2582493B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP28789491A JP2582493B2 (en) 1991-11-01 1991-11-01 Manufacturing method of artificial sand

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP28789491A JP2582493B2 (en) 1991-11-01 1991-11-01 Manufacturing method of artificial sand

Publications (2)

Publication Number Publication Date
JPH07112174A true JPH07112174A (en) 1995-05-02
JP2582493B2 JP2582493B2 (en) 1997-02-19

Family

ID=17723096

Family Applications (1)

Application Number Title Priority Date Filing Date
JP28789491A Expired - Lifetime JP2582493B2 (en) 1991-11-01 1991-11-01 Manufacturing method of artificial sand

Country Status (1)

Country Link
JP (1) JP2582493B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005103464A (en) * 2003-09-30 2005-04-21 Penta Ocean Constr Co Ltd Papermaking-sludge-ash-containing granule and method for manufacturing the same
CN105132072A (en) * 2015-08-25 2015-12-09 内蒙古天浩纸业有限公司 Waste treatment equipment for paper mill and waste treatment process method for paper mill

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6114100A (en) * 1984-06-29 1986-01-22 Kobe Steel Ltd Ni base coated electrode
JPS63197593A (en) * 1987-02-12 1988-08-16 Sintokogio Ltd Granulation of activated sludge incineration ash
JPH02126984A (en) * 1988-11-04 1990-05-15 Chugai Ro Co Ltd Method for forming sewage sludge incineration ash
JPH02126983A (en) * 1988-11-04 1990-05-15 Chugai Ro Co Ltd Method for forming sewage sludge incineration ash
JPH02175204A (en) * 1988-12-28 1990-07-06 Shin Nippon Kanetsu Kako Kk Manufacture of burnt matter by making use of burnt ash

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6114100A (en) * 1984-06-29 1986-01-22 Kobe Steel Ltd Ni base coated electrode
JPS63197593A (en) * 1987-02-12 1988-08-16 Sintokogio Ltd Granulation of activated sludge incineration ash
JPH02126984A (en) * 1988-11-04 1990-05-15 Chugai Ro Co Ltd Method for forming sewage sludge incineration ash
JPH02126983A (en) * 1988-11-04 1990-05-15 Chugai Ro Co Ltd Method for forming sewage sludge incineration ash
JPH02175204A (en) * 1988-12-28 1990-07-06 Shin Nippon Kanetsu Kako Kk Manufacture of burnt matter by making use of burnt ash

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005103464A (en) * 2003-09-30 2005-04-21 Penta Ocean Constr Co Ltd Papermaking-sludge-ash-containing granule and method for manufacturing the same
CN105132072A (en) * 2015-08-25 2015-12-09 内蒙古天浩纸业有限公司 Waste treatment equipment for paper mill and waste treatment process method for paper mill

Also Published As

Publication number Publication date
JP2582493B2 (en) 1997-02-19

Similar Documents

Publication Publication Date Title
WO2016011668A1 (en) Method for producing ceramic tiles using coal combustion waste
EP0626349A2 (en) Apparatus for making crystallized glass
US20240010571A1 (en) Elaboration of ceramic materials made from refractory waste for high-temperature thermal energy storage applications
CN107500724B (en) Shale ceramsite sand and preparation method thereof
JP2831009B2 (en) Population aggregate using municipal waste incineration ash and method for producing the same
FR3105975A1 (en) DEVELOPMENT OF CERAMIC MATERIALS MANUFACTURED FROM REFRACTORY WASTE FOR HIGH TEMPERATURE THERMAL ENERGY STORAGE APPLICATIONS
JP2582493B2 (en) Manufacturing method of artificial sand
JPH09100151A (en) Feedstock composition for producing ceramic product and ceramic product made therefrom
JPH1179808A (en) Artificial aggregate and its production
JP2001253740A (en) Artificial aggregate and its production process
JP4599802B2 (en) Lightweight aggregate foaming control method
JPH06227853A (en) Body composition for ceramic
JP2603599B2 (en) Artificial lightweight aggregate and manufacturing method thereof
JP2003238221A (en) Method of producing artificial aggregate
TWI686363B (en) Textile sludge reproduction-based light-weight pellet material, preparation method and manufacturing system thereof
JP3624033B2 (en) Artificial lightweight aggregate
JPH08253353A (en) Production of light-weight aggregate using incinerated ash of sewage sludge
TWI687388B (en) Clean water sludge reproduction-based light-weight pellet material, preparation method and manufacturing system thereof
JP2000007398A (en) Production of artificial aggregate
JP3702256B2 (en) Aggregate manufacturing method
JPH1072270A (en) Production of paving material excellent in water retentivity
JPH10226562A (en) Block for calcined building material with waste as main raw material
JP3635288B2 (en) Manufacturing method of artificial lightweight aggregate
US20120180598A1 (en) Process using fly ash to create chunks of raw material for iron or steel mill activities.
JP2001163648A (en) Producing method of artificial aggregate using waste incineration ash and artificial aggregate

Legal Events

Date Code Title Description
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 19960924