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JPH0359026B2 - - Google Patents
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JPH0359026B2 - - Google Patents

Info

Publication number
JPH0359026B2
JPH0359026B2 JP58067512A JP6751283A JPH0359026B2 JP H0359026 B2 JPH0359026 B2 JP H0359026B2 JP 58067512 A JP58067512 A JP 58067512A JP 6751283 A JP6751283 A JP 6751283A JP H0359026 B2 JPH0359026 B2 JP H0359026B2
Authority
JP
Japan
Prior art keywords
sludge
powder
raw material
combustible
amount
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
JP58067512A
Other languages
Japanese (ja)
Other versions
JPS59195571A (en
Inventor
Yoshihiko Kurashima
Katsushi Nagata
Yukio Furukawa
Takeshi Majima
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators 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 NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP58067512A priority Critical patent/JPS59195571A/en
Publication of JPS59195571A publication Critical patent/JPS59195571A/en
Publication of JPH0359026B2 publication Critical patent/JPH0359026B2/ja
Granted legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/02Agglomerated materials, e.g. artificial aggregates
    • C04B18/027Lightweight materials

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Civil Engineering (AREA)
  • Ceramic Engineering (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Organic Chemistry (AREA)
  • Porous Artificial Stone Or Porous Ceramic Products (AREA)
  • Compositions Of Oxide Ceramics (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は下水汚泥等の汚泥を原料とする軽量骨
材の製造法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to a method for producing lightweight aggregate using sludge such as sewage sludge as a raw material.

(従来技術) 従来、下水汚泥等の汚泥を原料として軽量骨材
を製造するには、造粒強度を増加させたり膨張性
や発泡性を増加させるためにベントナイト、粘
土、頁岩等の補助原料を原料汚泥に加えたのちさ
らにリグニン、CMC、PVA、水ガラス等の結合
剤を加えて造粒し、この造粒物をロータリーキル
ン、気流焼結炉等により外熱を利用して焼結する
方法であつたので、多量の補助原料と結合剤およ
び燃料を必要とし、設備コスト、ランニングコス
トおよび製造コストを上昇させるという欠点を有
するものであつた。また、汚泥を原料として軽量
骨材を製造する目的は主として発生する汚泥の体
積や重量を減少させかつ重金属が溶出しないよう
に安定化して、処分場の減少や確保を容易にする
ことや有効利用を図ることにあるのにもかかわら
ず、従来の製造法によれば汚泥の発生量に比較し
て軽量骨材の発生量が極めて多くなるという欠点
を有するものであつた。
(Prior art) Conventionally, in order to manufacture lightweight aggregates using sludge such as sewage sludge as a raw material, auxiliary materials such as bentonite, clay, and shale have been added to increase granulation strength, expandability, and foamability. After adding it to the raw material sludge, binders such as lignin, CMC, PVA, and water glass are added to granulate it, and the granules are sintered using external heat in a rotary kiln, airflow sintering furnace, etc. Since the method is hot, large amounts of auxiliary raw materials, binders and fuels are required, which has the drawback of increasing equipment costs, running costs and manufacturing costs. In addition, the purpose of producing lightweight aggregate using sludge as a raw material is to reduce the volume and weight of the generated sludge, stabilize it so that heavy metals do not elute, and facilitate the reduction and securing of disposal sites, as well as the effective use of sludge. However, the conventional manufacturing method has the disadvantage that the amount of lightweight aggregate generated is extremely large compared to the amount of sludge generated.

(発明の目的) 本発明は前記のような欠点を解消して補助原料
や結合剤、燃料などの使用量を少なくして設備コ
スト、ランニングコストおよび製造コストを低減
するとともに各種産業より多量に発生してその処
理処分に困つている汚泥の処分と有効利用とを図
ることのできる汚泥を原料とする軽量骨材の製造
法を目的として完成されたものである。
(Objective of the Invention) The present invention solves the above-mentioned drawbacks and reduces the amount of auxiliary raw materials, binders, fuel, etc. used, thereby reducing equipment costs, running costs, and manufacturing costs, as well as reducing the amount of materials generated in various industries. This was completed with the aim of producing a lightweight aggregate using sludge as a raw material, which would enable the disposal and effective use of sludge, which is difficult to treat and dispose of.

(発明の構成) 本発明は、汚泥焼却灰に乾燥汚泥粉末を主材と
する可燃物粉末を混合して発熱量を150〜
500Kcal/Kgに調整した原料粉末を所要の大きさ
に造粒したのち、この造粒物を下方吸引タイプの
焼結炉内に積重してその上方から着火し、上方か
ら空気を供給しつつ下方から吸引することによつ
て造粒物を動かすことなく、また外部から加熱す
ることなく自己燃焼により焼結させることを特徴
とするものである。
(Structure of the invention) The present invention mixes sludge incineration ash with combustible powder mainly composed of dried sludge powder to increase the calorific value from 150 to 150.
After the raw material powder adjusted to 500Kcal/Kg is granulated to the required size, the granules are stacked in a downward suction type sintering furnace, ignited from above, and air is supplied from above. It is characterized by sintering by self-combustion without moving the granules by suctioning from below and without heating from the outside.

(実施例) 次に、本発明の実施例を図示するフローシート
により詳細に説明すれば、1は汚泥処理場より発
生する脱水汚泥を焼却する焼結炉で、該焼結炉1
により焼結したのち粉砕または解砕して得た汚泥
焼却灰は多量の無機質粉末を含有した主原料とし
て、主原料サイロ3に貯留される。2は脱水汚泥
を乾燥させる乾燥機で、焼結炉1とは別に設けら
れて脱水汚泥の一部を焼結することなく乾燥し、
粉砕、分級した乾燥汚泥とし、該乾燥汚泥は副原
料としての可燃物粉末の主材として副原料サイロ
4に貯留され、また、必要に応じて乾燥汚泥に添
加されて副原料としての可燃物粉末の一部となる
微粉炭等の他の可燃物は別の副原料サイロ5に貯
留される。6は主原料サイロ3より供給される汚
泥焼却灰を分級する分級機で、主原料サイロ3に
貯留された汚泥焼却灰は分級機6により所定粒度
たとえば44μ以上の焼却灰粗粉と44μ以下の焼却
灰細粉とに分級されて前記副原料サイロ4,5に
並列させた焼却灰粗粉サイロ7と焼却灰細粉サイ
ロ8に貯留される。そして、焼却灰粗粉、焼却灰
細粉、乾燥汚泥および必要に応じて添加される他
の可燃物はいずれもこれらに含有される可燃物量
を測定され、造粒および燃焼の両面から考え最適
な混合比率が得られるように混合比率設定器9で
比率を設定し、その比率に合せて計量機10から
定量的に焼却灰粗粉と焼却灰細粉と乾燥汚泥およ
び他の可燃物が混合機11に投入されることによ
り主原料となる汚泥焼却灰に副原料となる可燃物
粉末を混合して発熱量を150〜500Kcal/Kgに調
整した原料粉末とする。なお、原料粉末中の可燃
物粉末量は一般的には5〜15重量%程度混合され
る場合が多い。次いで、この混合調整された原料
粉末は給水機12により給水されてパグミキサー
等の加湿混練機13により水分が5〜20重量%と
なるように加湿混練され、造粒のための一次凝集
が行なわれ、その後さらに造粒強度を上昇させる
ために原料粉末に対して所定割合たとえば2〜5
%の結合剤を結合剤サイロ14より供給し、次い
でパン型ペレタイザー等の造粒機15で加湿造粒
されて水分10〜25重量%で所要の大きさ例えば粒
径0.3〜20mmの造粒物に造粒する。次に、分級機
16で所定の粒径に分級した造粒物を底部に火格
子17を有する箱形の焼結台車21が多数のウイ
ンドボツクス22上を移動するようにした下方吸
引タイプの焼結炉の前記焼結台車21内に200〜
400mmとなるように充填機18により積重し、こ
の積重物が載装された焼結台車21を駆動装置2
3により着火室19に導き、積重物の表面部を着
火バーナー20により初期着火し、さらに、着火
室19より移行する間にウインドボツクス22か
ら排ガスフアン24により5〜150mmAqで下方吸
引しつつ通気して積重された造粒物中の可燃物粉
末を自己燃焼させれば、可燃物粉末は焼失すると
ともに造粒物中の汚泥焼却灰は焼結されて多孔質
粒状物化するから、この多孔質粒状物を焼結台車
21の反転によつて排出させて骨材サイロ25に
軽量骨材として貯留する。なお、前記焼結に必要
な条件としては温度をたとえば1000〜1100℃に数
分間維持するとともに下方に向つて高温熱風を流
して下層の造粒物を乾燥させ、この積重物の表層
部にある造粒物を燃焼させ、以後これに着火させ
て燃焼位置を順次下方に向つて移動させ、燃焼位
置が火格子17面まで下がつた時点で焼結台車2
1内の積重物の全層の焼結が完了する。また、原
料粉末の発熱量を限定したのは、汚泥中に含有さ
れる可燃物粉末の種類や量は季節や日時によりか
なり変動し、乾燥汚泥中の可燃物量と発熱量との
関係は一定でないから、汚泥重量に対する可燃物
量を重量百分率で表して限定しても適切でないか
らで、従つて、可燃物の種類や量がほぼ定まつて
いる汚泥については可燃物量を汚泥重量に対する
重量百分率で管理することによつて発熱量の管理
を行うこともできる。
(Example) Next, an example of the present invention will be described in detail with reference to a flow sheet illustrating a sintering furnace 1 for incinerating dehydrated sludge generated from a sludge treatment plant.
The sludge incineration ash obtained by sintering and crushing or crushing is stored in the main raw material silo 3 as a main raw material containing a large amount of inorganic powder. 2 is a dryer for drying dehydrated sludge, which is installed separately from the sintering furnace 1 and dries a part of the dehydrated sludge without sintering;
The dried sludge is crushed and classified into dry sludge, and the dried sludge is stored in the auxiliary raw material silo 4 as the main material for combustible powder as an auxiliary raw material, and is added to the dried sludge as needed to form combustible powder as an auxiliary raw material. Other combustible materials such as pulverized coal, which become part of the pulverized coal, are stored in another auxiliary raw material silo 5. 6 is a classifier for classifying the sludge incineration ash supplied from the main raw material silo 3, and the sludge incineration ash stored in the main raw material silo 3 is divided into predetermined particle sizes, e.g. coarse incinerated ash powder of 44μ or more, and incineration ash coarse powder of 44μ or less. The incinerated ash is classified into fine incinerated ash powder and stored in the incinerated ash coarse powder silo 7 and the incinerated ash fine powder silo 8 which are arranged in parallel with the auxiliary raw material silos 4 and 5. Then, the amount of combustibles contained in the coarse incinerated ash powder, fine incinerated ash powder, dried sludge, and other combustibles added as necessary is measured, and the optimal amount is determined from both granulation and combustion perspectives. The ratio is set using the mixing ratio setting device 9 so that the desired mixing ratio can be obtained, and according to the ratio, the coarse incinerated ash powder, the fine incinerated ash powder, the dried sludge, and other combustible materials are quantitatively mixed from the weighing machine 10 into the mixer. 11, sludge incineration ash, which serves as the main raw material, is mixed with combustible powder, which serves as an auxiliary raw material, to obtain a raw material powder with a calorific value adjusted to 150 to 500 Kcal/Kg. Incidentally, the amount of combustible powder in the raw material powder is generally about 5 to 15% by weight in many cases. Next, this mixed and adjusted raw material powder is supplied with water by a water supply machine 12 and humidified and kneaded by a humidifying kneader 13 such as a pug mixer so that the water content becomes 5 to 20% by weight, and primary aggregation for granulation is performed. After that, in order to further increase the granulation strength, a predetermined proportion, for example 2 to 5, is added to the raw material powder.
% binder is supplied from a binder silo 14, and then humidified and granulated in a granulator 15 such as a pan-type pelletizer to form granules with a moisture content of 10 to 25% by weight and a desired size, for example, a particle size of 0.3 to 20 mm. Granulate into Next, the granules classified into a predetermined particle size by the classifier 16 are transferred to a downward suction type sintering machine in which a box-shaped sintering cart 21 having a grate 17 at the bottom moves over a large number of wind boxes 22. 200~ in the sintering cart 21 of the sintering furnace
The filling machine 18 stacks the materials to a thickness of 400 mm, and the sintering cart 21 loaded with the stacked materials is transferred to the drive device 2.
3 to the ignition chamber 19, the surface of the stack is initially ignited by the ignition burner 20, and further, while it is being transferred from the ignition chamber 19, it is ventilated while being suctioned downward at 5 to 150 mmAq from the wind box 22 by the exhaust gas fan 24. If the combustible powder in the piled up granules is self-combusted, the combustible powder will be burned out and the sludge incineration ash in the granules will be sintered and become porous granules. The heavy granules are discharged by reversing the sintering cart 21 and stored in the aggregate silo 25 as lightweight aggregate. The conditions necessary for the sintering are, for example, maintaining the temperature at 1000 to 1100°C for several minutes, blowing high-temperature hot air downward to dry the granules in the lower layer, and applying heat to the surface layer of this stack. A certain granule is combusted, and then it is ignited to move the combustion position downward one by one, and when the combustion position reaches the grate 17 surface, the sintering cart 2
Sintering of all layers of the stack in 1 is completed. In addition, the calorific value of the raw material powder was limited because the type and amount of combustible powder contained in sludge varies considerably depending on the season and date and time, and the relationship between the amount of combustible material in dried sludge and the calorific value is not constant. Therefore, it is not appropriate to limit the amount of combustibles to the sludge weight by expressing it as a weight percentage. Therefore, for sludge where the type and amount of combustibles are almost fixed, the amount of combustibles should be managed as a weight percentage to the sludge weight. By doing so, it is also possible to manage the amount of heat generated.

本発明において利用出来る原料粉末は可燃物を
ほとんど含有しないもので都市ごみ等の廃棄物や
下水汚泥等の各種汚泥の焼却灰のように未燃炭素
や有機物を含有するものでもよく、これらのもの
に乾燥廃棄物、乾燥汚泥、おが粉、微粉炭、プラ
スチツク粉末等の可燃物粉末を添加混合して原料
粉末中の発熱量を150〜500Kcal/Kgに調整して
おくもので、発熱量を前記の範囲のものに限定し
た理由は、発熱量が15Kcal/Kg未満であると造
粒物が自己燃焼して焼結するのに必要なエネルギ
ーが不足し、未燃部分が多くなつて圧壊強度が低
下するので、これを防止するには高温熱風等の外
部エネルギー供給することが必要でこのための設
備及び燃費を必要とし製品コストの増大をまねく
ものであり、他方、発熱量が500Kcal/Kgを越え
ると造粒物が溶融し、クリンカーが生成して融着
するので多孔体として不適当なものとなるばかり
でなく焼結台車からの搬出も困難となつて好まし
くないからである。さらに、実施例において汚泥
焼却灰として焼却灰粗粉と焼却灰細粉とを混合す
るのは、汚泥焼却灰の粒度と可燃物量との間には
一般に粗粉中に可燃物量が多く、細粉中には可燃
物量が少ないという関係にあることと、細粉と粗
粉とが適度に混合されている方が成形しやすいか
らであつて、汚泥焼却灰の粒度や発熱量によつて
は所定粒度以下や以上のものをカツトするだけで
もよいし極端な場合にはそのままでもよい。ま
た、造粒時並びに乾燥時に造粒物が簡単に破壊し
ない程度の造粒強度を持たせるためには実施例の
ようにたとえばCMC、PVA、水ガラス等の結合
剤を原料粉末に対して0〜5重量%程度添加して
造粒物表面にコーテイングしたり混合したりする
ことが好ましい。なお、可燃物粉末は脱水汚泥を
焼却して得た汚泥焼却灰を主原料とし、前記脱水
汚泥の一部を乾燥して得た乾燥汚泥を副原料とし
てこれを混合造粒焼結して軽量骨材を製造すれ
ば、焼却工程で発生する余剰熱を乾燥工程や焼却
工程に循環して利用することができるので系とし
て極めて熱効率が良くて省エネルギー上好ましい
が、ごみ焼却灰と下水汚泥焼却灰とを主原料と
し、乾燥汚泥と微粉炭とを副原料とするなど発生
汚泥量、汚泥性状や最終製品の性状等によつて数
種の主原料と数種の複原料とを組合せて軽量骨材
を製造してもよい。
The raw material powder that can be used in the present invention contains almost no combustible materials, and may also contain unburned carbon and organic matter, such as incineration ash of various sludges such as municipal waste and sewage sludge. The calorific value of the raw material powder is adjusted to 150 to 500 Kcal/Kg by adding and mixing dry waste, dry sludge, sawdust, pulverized coal, plastic powder, and other combustible powder. The reason for limiting the above range is that if the calorific value is less than 15 Kcal/Kg, the energy required for self-combustion and sintering of the granules will be insufficient, and the unburned portion will increase, resulting in a decrease in compressive strength. To prevent this, it is necessary to supply external energy such as high-temperature hot air, which requires equipment and fuel consumption, leading to an increase in product cost. If the temperature exceeds this value, the granules will melt and clinker will form and fuse, making it unsuitable as a porous body, and also making it difficult to transport from the sintering cart, which is undesirable. Furthermore, in the Examples, the reason why incinerated ash coarse powder and incinerated ash fine powder are mixed as sludge incinerated ash is that there is a difference between the particle size of sludge incinerated ash and the amount of combustible matter, since the amount of combustible matter in the coarse powder is generally large, and the fine powder is This is because there is a relationship between the amount of combustible materials in the sludge incineration ash and the fact that it is easier to mold it when a moderate amount of fine powder and coarse powder are mixed. It may be sufficient to simply cut particles smaller than or larger than the particle size, or in extreme cases, it may be left as is. In addition, in order to have granulation strength to the extent that the granules do not easily break during granulation and drying, binders such as CMC, PVA, and water glass are added to the raw material powder as shown in the examples. It is preferable to add about 5% by weight and coat the surface of the granules or mix them. The combustible powder is made from sludge incineration ash obtained by incinerating dehydrated sludge as the main raw material, and dried sludge obtained by drying a part of the dehydrated sludge as an auxiliary raw material, which is mixed and granulated and sintered to make it lightweight. If aggregate is manufactured, surplus heat generated in the incineration process can be recycled and used in the drying process and incineration process, so the system has extremely high thermal efficiency and is preferable in terms of energy conservation. The main raw material is dried sludge and pulverized coal as secondary raw materials, and several types of main raw materials and several types of composite materials are combined depending on the amount of sludge generated, the properties of the sludge, and the properties of the final product. Materials may also be manufactured.

(発明の効果) 本発明は以上の説明から明らかなように、汚泥
焼却灰に乾燥汚泥粉末を主材とする可燃物粉末を
発熱量が150〜500Kcal/Kgとなるように混合調
整して原料粉末とし、次いでこの原料粉末を造粒
後焼結炉内に積重し自己燃焼により焼結させるこ
とにより軽量骨材を得ようとするもので、原料汚
泥以外に多量の補助原料や結合剤を必要とせず、
原料汚泥を焼却した汚泥焼却灰と原料汚泥を乾燥
した乾燥汚泥との組合せのようにほとんど原料汚
泥のみで軽量骨材を製造できるため、処分汚泥量
を増加させることが少なく、しかも、原料汚泥中
の可燃物を有効に利用することができるために燃
料を大幅に節減して製造コストを低減することが
でき、しかも、各種産業から多量に発生して処分
に困つている都市ごみ、下水汚泥等の焼却灰、硅
砂等の無機質廃棄物と下水汚泥、上水汚泥等の乾
燥汚泥がおが粉、微粉炭等の有機質廃棄物の処分
と有効利用とを同時にはかることができる大きな
利点があり、本発明によつて得られる軽量骨材が
強度的に優れたものとなるので建材、吸音材、断
熱材等幅広い用途を持つ利点と相俟ち業界の発展
に寄与するところ極めて大なものである。
(Effects of the Invention) As is clear from the above description, the present invention is made by mixing and adjusting combustible powder mainly composed of dried sludge powder with sludge incineration ash so that the calorific value is 150 to 500 Kcal/Kg. This method aims to obtain lightweight aggregate by pulverizing the raw material powder, stacking it in a sintering furnace after granulating it, and sintering it by self-combustion.In addition to the raw material sludge, a large amount of auxiliary raw materials and binders are used. without needing,
Since lightweight aggregates can be produced using almost only raw material sludge, such as a combination of sludge incineration ash obtained by incinerating raw material sludge and dried sludge obtained by drying raw material sludge, there is little increase in the amount of sludge to be disposed of, and moreover, there is no need to increase the amount of sludge in the raw material sludge. This makes it possible to effectively utilize combustible materials such as municipal waste, sewage sludge, etc., which are generated in large quantities from various industries and are difficult to dispose of. It has the great advantage that inorganic waste such as incineration ash and silica sand, and dried sludge such as sewage sludge and clean water sludge can be used to dispose and effectively utilize organic waste such as sawdust and pulverized coal at the same time. Since the lightweight aggregate obtained by the present invention has excellent strength, it has the advantage of being used in a wide range of applications such as building materials, sound absorbing materials, and heat insulating materials, and together with this, it will greatly contribute to the development of the industry. .

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

図面は本発明の実施例を示すフローシートであ
る。
The drawing is a flow sheet showing an embodiment of the invention.

Claims (1)

【特許請求の範囲】[Claims] 1 汚泥焼却灰に乾燥汚泥粉末を主材とする可燃
物粉末を混合して発熱量を150〜500Kcal/Kgに
調整した原料粉末を所要の大きさに造粒したの
ち、この造粒物を下方吸引タイプの焼結炉内に積
重してその上方から着火し、上方から空気を供給
しつつ下方から吸引することによつて造粒物を動
かすことなく、また外部から加熱することなく自
己燃焼により焼結させることを特徴とする汚泥を
原料とする軽量骨材の製造法。
1 Mix sludge incineration ash with combustible powder mainly composed of dried sludge powder to adjust the calorific value to 150 to 500 Kcal/Kg, granulate the raw material powder to the required size, and then pour the granulated material downward. They are stacked in a suction type sintering furnace and ignited from above, and by supplying air from above and suctioning from below, self-combustion occurs without moving the granules or heating them from the outside. A method for producing lightweight aggregate using sludge as a raw material, which is characterized by sintering.
JP58067512A 1983-04-15 1983-04-15 Manufacture of lightweight aggregate from sludge Granted JPS59195571A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58067512A JPS59195571A (en) 1983-04-15 1983-04-15 Manufacture of lightweight aggregate from sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58067512A JPS59195571A (en) 1983-04-15 1983-04-15 Manufacture of lightweight aggregate from sludge

Publications (2)

Publication Number Publication Date
JPS59195571A JPS59195571A (en) 1984-11-06
JPH0359026B2 true JPH0359026B2 (en) 1991-09-09

Family

ID=13347103

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58067512A Granted JPS59195571A (en) 1983-04-15 1983-04-15 Manufacture of lightweight aggregate from sludge

Country Status (1)

Country Link
JP (1) JPS59195571A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS59195572A (en) * 1983-04-15 1984-11-06 日本碍子株式会社 Manufacture of lightweight aggregate
JPS63123845A (en) * 1986-11-12 1988-05-27 日本碍子株式会社 Method for manufacturing lightweight aggregate using incineration ash as raw material
JPH0684262B2 (en) * 1988-11-09 1994-10-26 稔也 田中 Manufacturing method of ceramics using sewage sludge incineration ash
JP2776896B2 (en) * 1989-06-28 1998-07-16 中外炉工業株式会社 Fired body of sewage sludge incineration ash

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5830380A (en) * 1981-08-17 1983-02-22 Nittetsu Mining Co Ltd Treatment for incineration ash of sewage sludge

Also Published As

Publication number Publication date
JPS59195571A (en) 1984-11-06

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