JPH07313950A - Granular material made from waste and waste treatment method - Google Patents

Granular material made from waste and waste treatment method

Info

Publication number
JPH07313950A
JPH07313950A JP11512594A JP11512594A JPH07313950A JP H07313950 A JPH07313950 A JP H07313950A JP 11512594 A JP11512594 A JP 11512594A JP 11512594 A JP11512594 A JP 11512594A JP H07313950 A JPH07313950 A JP H07313950A
Authority
JP
Japan
Prior art keywords
waste
limestone
sludge
water treatment
water
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
JP11512594A
Other languages
Japanese (ja)
Other versions
JP3261601B2 (en
Inventor
Yuji Tsukamoto
裕二 塚本
Takuro Murai
卓郎 村井
Naoyuki Shimoda
直之 下田
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 Materials Corp
Original Assignee
Mitsubishi Materials 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 Mitsubishi Materials Corp filed Critical Mitsubishi Materials Corp
Priority to JP11512594A priority Critical patent/JP3261601B2/en
Publication of JPH07313950A publication Critical patent/JPH07313950A/en
Application granted granted Critical
Publication of JP3261601B2 publication Critical patent/JP3261601B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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 recycle city waste and water treatment sludge as concrete aggregate, roadbed material, or reclaiming material by treating the waste easily and efficiently. CONSTITUTION:A crushed mixture of city waste and/or water treatment sludge with limestone or a mixture of crushed waste and crushed limestone is burned at 1000-1500 deg.C in a rotary furnace into compact particles 40 mm or less in diameter. Since the city waste and the water treatment sludge are a clay-type material, the particles have a property of cement clinker. The particles have enough strength and are free from the elution of harmful substances so that they can be utilized effectively as concrete aggregate, roadbed material, reclaiming material, etc.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は廃棄物より製造した粒状
物及び廃棄物処理方法に係り、特に、都市ゴミや水処理
汚泥を処理してコンクリート骨材、路盤材、埋め戻し材
等としての有効利用を図る、廃棄物より製造した粒状物
及び廃棄物処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a granular material produced from waste and a method for treating the waste, and more particularly, as a concrete aggregate, a roadbed material, a backfill material, etc. by treating municipal waste and water treatment sludge. The present invention relates to a granular material produced from waste and a waste treatment method for effective utilization.

【0002】[0002]

【従来の技術】都市ゴミは焼却処理後、或いは焼却処理
されることなくそのまま埋め立て処分されている。近
年、都市ゴミの発生量は増々増加する傾向にあり、焼却
コストの高騰、埋立地の不足が問題視されている。
2. Description of the Related Art Municipal refuse is either incinerated or landfilled without being incinerated. In recent years, the amount of municipal waste generated has been increasing, and soaring incineration costs and shortage of landfills have become a problem.

【0003】一方、下水処理汚泥や上水処理汚泥等の水
処理汚泥は、各水処理場から大量に排出される。これら
水処理汚泥は、脱水後焼却され、或いは焼却処理される
ことなく埋め立て処分されており、その発生量が莫大な
量であることから、埋立地の不足が問題となっている。
On the other hand, a large amount of water treatment sludge such as sewage treatment sludge and tap water treatment sludge is discharged from each water treatment plant. These water-treated sludges are dehydrated and then incinerated, or they are disposed of in landfill without being incinerated, and the amount of the generated sludge is enormous. Therefore, the shortage of landfill is a problem.

【0004】そこで、最近になって、都市ゴミや水処理
汚泥の有効再利用を図るための研究開発がなされるよう
になり、特に下水汚泥焼却灰については、これを成形、
焼成して軽量骨材等を製造する方法が提案されている
(特公昭61−14099号、同61−14100
号)。
Therefore, recently, research and development have been carried out for the effective reuse of municipal waste and water-treated sludge. Particularly, for sewage sludge incineration ash, this is molded,
A method of producing a lightweight aggregate by firing has been proposed (Japanese Patent Publication Nos. 61-14099 and 61-14100).
issue).

【0005】[0005]

【発明が解決しようとする課題】上記従来の方法では、
下水汚泥を脱水、焼成して焼却灰とする必要があり、下
水汚泥をそのまま用いることはできない。
SUMMARY OF THE INVENTION In the above conventional method,
Sewage sludge needs to be dehydrated and fired to form incinerated ash, and sewage sludge cannot be used as it is.

【0006】一方、都市ゴミについては、一部肥料化な
どが提案されているが、大量の都市ゴミを有効再利用す
るための実用的な方法が提案されていないのが現状であ
る。
[0006] On the other hand, with respect to municipal waste, some proposals such as fertilization have been proposed, but at present, no practical method has been proposed for effectively reusing a large amount of municipal waste.

【0007】本発明は、上記従来の実情に鑑みてなされ
たものであって、都市ゴミや水処理汚泥を容易かつ効率
的に処理してコンクリート骨材、路盤材、埋め戻し材等
として有効再利用することを可能とする、廃棄物より製
造した粒状物及び廃棄物処理方法を提供することを目的
とする。
[0007] The present invention has been made in view of the above-mentioned conventional circumstances, and is effective as a concrete aggregate, a roadbed material, a backfill material, etc. by easily and efficiently treating municipal waste and water treatment sludge. It is an object of the present invention to provide a granular material produced from waste and a method of treating the waste, which can be utilized.

【0008】[0008]

【課題を解決するための手段】請求項1の廃棄物より製
造した粒状物は、都市ゴミ及び/又は水処理汚泥と石灰
石とを混合粉砕した後、回転式焼成炉にて1000〜1
500℃で焼成して得られる、粒径40mm以下の焼き
締まった粒状体よりなることを特徴とする。
The particulate matter produced from the waste according to claim 1 is a mixture of municipal waste and / or water treatment sludge and limestone, which is then crushed in a rotary calcination furnace to 1000-1.
It is characterized in that it is composed of a hardened granular material having a particle diameter of 40 mm or less obtained by firing at 500 ° C.

【0009】請求項2の廃棄物より製造した粒状物は、
都市ゴミ及び/又は水処理汚泥と石灰石とを各々粉砕し
た後混合し、次いで、回転式焼成炉にて1000〜15
00℃で焼成して得られる、粒径40mm以下の焼き締
まった粒状体よりなることを特徴とする。
The particulate matter produced from the waste of claim 2 is
Municipal refuse and / or water treatment sludge and limestone are crushed and mixed together, and then 1000 to 15 in a rotary firing furnace.
It is characterized in that it is composed of a hardened granular material having a particle diameter of 40 mm or less obtained by firing at 00 ° C.

【0010】請求項3の廃棄物処理方法は、都市ゴミ及
び/又は水処理汚泥と石灰石とを混合粉砕した後、回転
式焼成炉にて1000〜1500℃で焼成し、粒径40
mm以下の焼き締まった粒状体とすることを特徴とす
る。
According to a third aspect of the waste treatment method of the present invention, municipal waste and / or water treatment sludge and limestone are mixed and pulverized and then calcinated in a rotary calcination furnace at 1000 to 1500 ° C. to obtain a particle size of 40.
It is characterized in that it is made into a granular body of which the size is not more than mm.

【0011】請求項4の廃棄物処理方法は、都市ゴミ及
び/又は水処理汚泥と石灰石とを各々粉砕した後混合
し、次いで、回転式焼成炉にて1000〜1500℃で
焼成し、粒径40mm以下の焼き締まった粒状体とする
ことを特徴とする。
In the waste treatment method of claim 4, municipal waste and / or water treatment sludge and limestone are crushed and mixed, and then calcinated in a rotary calcination furnace at 1000 to 1500 ° C. to obtain a particle size. It is characterized in that it is a compacted grain of 40 mm or less.

【0012】以下に本発明を詳細に説明する。The present invention will be described in detail below.

【0013】本発明においては、まず、 都市ゴミ及び/又は水処理汚泥と石灰石とをミル等
に投入して混合粉砕する。 或いは 都市ゴミ及び/又は水処理汚泥と石灰石とを各々別
々に粉砕した後、混合する(以下、都市ゴミ及び/又は
水処理汚泥と石灰石との混合粉砕に対して、都市ゴミ及
び/又は水処理汚泥と石灰石とを各々別々に混合する場
合を、「個別粉砕」と称する場合がある。)。 この混合粉砕又は粉砕に当り、都市ゴミ及び/又は水処
理汚泥は予め乾燥しておくのが好ましい。
In the present invention, first, municipal waste and / or water treatment sludge and limestone are put into a mill or the like and mixed and ground. Alternatively, the municipal waste and / or water treatment sludge and the limestone are separately crushed and then mixed (hereinafter, for the mixed pulverization of the municipal waste and / or water treatment sludge and the limestone, the municipal waste and / or the water treatment is performed. The case where sludge and limestone are mixed separately may be referred to as "individual crushing".). In this mixed pulverization or pulverization, it is preferable to dry the municipal waste and / or the water-treated sludge in advance.

【0014】なお、本発明において、都市ゴミとは、台
所ゴミ、紙ゴミ、木片、布、その他の可燃ゴミである
が、プラスチック、発泡スチロール、金属等の不燃ゴミ
が若干含まれていても支障はない。
In the present invention, the municipal waste refers to kitchen waste, paper waste, wood chips, cloth, and other combustible waste, but even if a small amount of non-combustible waste such as plastic, styrofoam, and metal is contained, no problem occurs. Absent.

【0015】一方、水処理汚泥とは、下水処理場、上水
処理場等の水処理場から排出される下水処理汚泥、上水
処理汚泥等の水処理汚泥である。
On the other hand, the water treatment sludge is a water treatment sludge such as a sewage treatment sludge or a water treatment sludge discharged from a water treatment plant such as a sewage treatment plant or a water treatment plant.

【0016】これら都市ゴミ及び/又は水処理汚泥或い
はその粉砕物に混合する石灰石の混合割合は、都市ゴミ
及び/又は水処理汚泥或いはその粉砕物の乾燥重量に対
して等量以上、好ましくは都市ゴミ及び/又は水処理汚
泥或いはその粉砕物の乾燥重量の1〜20倍である。石
灰石の割合が都市ゴミ及び/又は水処理汚泥或いはその
粉砕物の乾燥重量の等量未満であると後工程の焼成によ
り生成するクリンカー鉱物の生成量が少なくなり、得ら
れる粒状体が脆くなって、コンクリート骨材、路盤材、
埋め戻し材等の用途に適さなくなる。石灰石の混合割合
が多過ぎても添加による効果に大差はなく、都市ゴミや
水処理汚泥の処理量当りの石灰石使用量が増え、処理コ
ストが高くつき好ましくない。
The mixing ratio of limestone to be mixed with these municipal solid waste and / or water treatment sludge or its crushed product is equal to or more than the dry weight of the municipal waste and / or water treated sludge or its crushed product, preferably urban. It is 1 to 20 times the dry weight of waste and / or water-treated sludge or its crushed product. If the proportion of limestone is less than the dry weight of municipal waste and / or water-treated sludge or its crushed product, the amount of clinker mineral produced by firing in the subsequent step will be small and the resulting granules will become brittle. , Concrete aggregate, roadbed material,
It becomes unsuitable for applications such as backfill materials. Even if the mixing ratio of limestone is too large, the effect of the addition is not so different, the amount of limestone used per amount of treated municipal waste or water treatment sludge increases, and the treatment cost becomes high, which is not preferable.

【0017】なお、この混合粉砕或いは個別粉砕の程度
に特に制限はないが、通常の場合、都市ゴミ及び/又は
水処理汚泥の乾燥物のみ或いはこの乾燥物と石灰石とを
ミルに投入して10〜20分程度処理し、粒径20〜1
00μ程度の粉砕物とするのが好ましい。
The degree of the mixed pulverization or the individual pulverization is not particularly limited, but in the usual case, only the dried product of the municipal waste and / or the water-treated sludge or the dried product and limestone is charged into a mill to obtain 10 ~ 20 minutes treatment, particle size 20 ~ 1
It is preferable to use a pulverized product of about 00 μ.

【0018】都市ゴミ及び/又は水処理汚泥と石灰石と
を混合粉砕して得られた混合粉砕物、或いは、都市ゴミ
及び/又は水処理汚泥と石灰石とを個別粉砕した後混合
して得られた粉砕混合物は、次いで、回転型造粒焼成炉
等の回転式焼成炉(ロータリーキルン)に投入して10
00〜1500℃で焼成する。
A mixed pulverized product obtained by mixing and pulverizing municipal waste and / or water-treated sludge and limestone, or obtained by individually pulverizing and mixing urban trash and / or water-treated sludge and limestone. The pulverized mixture is then charged into a rotary kiln (rotary kiln) such as a rotary granulation kiln to obtain 10
Bake at 00 to 1500 ° C.

【0019】この焼成温度が1000℃未満では十分に
焼き締った粒状体を得ることができず、コンクリート骨
材、路盤材、埋め戻し材等としての用途に適さなくな
る。また、焼成温度が1500℃を超えても焼き締り状
態に大差はなく、焼成コストが高くつくことから、焼成
温度は1000〜1500℃とする。
If the firing temperature is less than 1000 ° C., it is not possible to obtain a sufficiently hardened granular material, which makes it unsuitable for use as a concrete aggregate, a roadbed material, a backfill material and the like. Further, even if the firing temperature exceeds 1500 ° C., there is no great difference in the tightly closed state, and the firing cost is high, so the firing temperature is set to 1000 to 1500 ° C.

【0020】なお、特に十分に焼き締った粒状体を得る
ためには、焼成温度は1200℃以上とするのが好まし
い。この焼成に当り、焼成原料中にアルカリ分を含むガ
ラスカレット等を配合することにより焼き締り状態を改
善することができ、従って、焼成温度を下げることがで
きる。例えば、焼成原料中に5重量%以下の範囲でガラ
スカレットを混合することにより、焼成温度1000℃
程度で十分に焼き締った粒状体を得ることができる。
The firing temperature is preferably 1200 ° C. or higher in order to obtain a particularly well-pressed granular material. At the time of this firing, by mixing glass cullet containing an alkali component in the firing raw material, it is possible to improve the tightness of the fire and thus to lower the firing temperature. For example, by mixing the glass cullet in the firing raw material in an amount of 5% by weight or less, the firing temperature is 1000 ° C.
Granules that have been sufficiently baked can be obtained to some extent.

【0021】得られた粒状体は、通常の場合、粒径0.
5〜40mmの範囲で、平均粒径は25mmのものであ
り、これをそのままコンクリート骨材、路盤材、埋め戻
し材等として用いることができる。
The resulting granules usually have a particle size of 0.
In the range of 5 to 40 mm, the average particle diameter is 25 mm, which can be used as it is as a concrete aggregate, a roadbed material, a backfill material, or the like.

【0022】本発明により得られる粒状体は、粘土系物
質である都市ゴミ及び/又は水処理汚泥と石灰石との焼
成物であるため、組成的にはセメント類似物質であり、
従って湿潤すると固化する性状を有し、コンクリート骨
材、路盤材、埋め戻し材等として極めて有効に使用する
ことができる。即ち、例えば、この粒状体を路面等に敷
設し、その後水を散布すると粒状体同志が接合して固化
し、歩行又は走行に十分な強度を有する路面又は下地面
を形成することができる。
The granular material obtained according to the present invention is a cement-like substance in terms of composition, since it is a burned product of municipal waste and / or water-treated sludge, which is a clay-based substance, and limestone.
Therefore, it has a property of solidifying when wet, and can be extremely effectively used as a concrete aggregate, a roadbed material, a backfill material and the like. That is, for example, when this granular body is laid on a road surface or the like, and then water is sprinkled, the granular bodies are bonded and solidified to form a road surface or a base surface having sufficient strength for walking or running.

【0023】ところで、都市ゴミ及び/又は水処理汚泥
には、一般に揮発性のPb,Zn,Cd等の金属化合物
が含有されている。
By the way, municipal waste and / or water treatment sludge generally contains volatile metal compounds such as Pb, Zn and Cd.

【0024】本発明においては、焼成に当り、プレヒー
タ付ロータリーキルンを用い、これらの揮発性金属化合
物をプレヒータで抽気し、その後温度制御のもとに冷却
して各揮発性金属化合物を濃縮、回収することもでき
る。
In the present invention, in firing, a rotary kiln with a preheater is used, and these volatile metal compounds are extracted by the preheater and then cooled under temperature control to concentrate and recover each volatile metal compound. You can also

【0025】[0025]

【作用】都市ゴミ及び水処理汚泥は粘土系物質であるた
め、これに石灰石を混合して焼成することにより、セメ
ントと同様にクリンカー鉱物が生成してクリンカー状の
粒状体が得られる。
Since municipal waste and water-treated sludge are clay-based substances, clinker minerals are produced in the same manner as cement and clinker-like particles are obtained by mixing limestone with this and firing.

【0026】得られた粒状体は十分な強度を有し、ま
た、有害物質の溶出の問題もなく、コンクリート骨材、
路盤材、埋め戻し材等として有効に利用できる。
The obtained granules have sufficient strength, and there is no problem of elution of harmful substances.
It can be effectively used as a roadbed material and backfill material.

【0027】特に、この粒状体は、湿潤すると固化する
性状を有し、路面施工等に極めて有用である。
In particular, this granular material has the property of solidifying when wet, and is extremely useful for road surface construction and the like.

【0028】[0028]

【実施例】以下に実施例及び実験例を挙げて本発明をよ
り具体的に説明する。
EXAMPLES The present invention will be described more specifically with reference to Examples and Experimental Examples.

【0029】なお、実施例において用いた都市ゴミは、
一般の可燃都市ゴミであり、予め100℃で30分間乾
燥されたものである。また、水処理汚泥(下水処理汚
泥)は、100℃で30分間乾燥したものであり、表1
における都市ゴミ、水処理汚泥重量は乾燥重量で示して
ある。
The municipal waste used in the examples is
It is general combustible municipal waste, which has been previously dried at 100 ° C for 30 minutes. The water-treated sludge (sewage-treated sludge) was dried at 100 ° C. for 30 minutes.
The weight of municipal waste and water treatment sludge in is shown as dry weight.

【0030】実施例1 都市ゴミ及び/又は水処理汚泥(乾燥品)と石灰石とを
表1に示す割合でミルにて15分間混合粉砕して平均粒
径50μの粉砕物を得た。この粉砕物をロータリーキル
ンに投入し(なお、No.3においては、ガラスカレッ
トを全焼成原料に対して3重量%混合した。)、表1に
示す温度で表1に示す時間焼成し、表1に示す平均粒径
の粒状体を得た。得られた粒状体のうち粒径5mm以下
を細骨材、粒径5mm以上を粗骨材とした下記配合のコ
ンクリート供試体について、下記方法により圧潰強度を
測定すると共に溶出試験を行い、結果を表1に示した。
Example 1 Municipal waste and / or water-treated sludge (dry product) and limestone were mixed and pulverized in a mill at a ratio shown in Table 1 for 15 minutes to obtain a pulverized product having an average particle size of 50μ. This pulverized product was put into a rotary kiln (in the case of No. 3, glass cullet was mixed in an amount of 3% by weight with respect to all the firing materials), and the mixture was fired at the temperature shown in Table 1 for the time shown in Table 1. A granular material having an average particle size shown in was obtained. Among the obtained granules, the crushing strength was measured by the following method and the elution test was performed on the concrete specimens having the following composition, in which the particle diameter of 5 mm or less was fine aggregate and the particle diameter of 5 mm or more was coarse aggregate, and the elution test was performed. The results are shown in Table 1.

【0031】なお、比較のため、石灰石を用いなかった
こと以外は同様にして粉砕、焼成したところ、都市ゴミ
についても水処理汚泥についても粒状体を得ることはで
きなかった。
For comparison, when crushing and firing were carried out in the same manner except that limestone was not used, it was not possible to obtain particulate matter from either municipal waste or water-treated sludge.

【0032】コンクリート配合(重量部) セメント:300kg 細骨材(粒径5mm以下の粒状体): 700kg 粗骨材(粒径5mm以上の粒状体):1050kg 水:165kg圧潰強度測定方法 JIS A 1108に規定された方法により実施し
た。
Mixing of concrete (parts by weight) Cement: 300 kg Fine aggregate (granular particles with a particle size of 5 mm or less): 700 kg Coarse aggregate (granular particles with a particle size of 5 mm or more): 1050 kg Water: 165 kg Crush strength measuring method JIS A 1108 It was carried out by the method specified in 1.

【0033】溶出試験方法 昭和48年環境庁告示第13号,産業廃棄物に含まれる
金属等の検定方法により検液を作成し、JIS K 0
102工場排水の試験方法により微量成分の溶出量を定
量した。
Dissolution test method A test solution was prepared according to JIS K No. 13 of 1973, a test method for metals contained in industrial waste, and JIS K 0
The amount of trace components eluted was determined by the test method of 102 factory wastewater.

【0034】[0034]

【表1】 [Table 1]

【0035】実験例1 実施例1で得られた、各粒状物について、舗装要綱で規
定された方法により一軸圧縮強度及び修正CBRを測定
した。
Experimental Example 1 The uniaxial compressive strength and the modified CBR of each of the granules obtained in Example 1 were measured by the method specified in the paving outline.

【0036】その結果、表2に示す通り、いずれの場合
も十分な性能を有し、路面材等として用いた場合、耐久
性に優れた路面を形成できることが確認された。
As a result, as shown in Table 2, it was confirmed that a road surface having sufficient performance in any case and having excellent durability can be formed when used as a road surface material or the like.

【0037】[0037]

【表2】 [Table 2]

【0038】なお、都市ゴミ及び/又は水処理汚泥(乾
燥品)を予めミルで平均粒径50μに粉砕した後、平均
粒径50μの石灰石と混合したこと以外は実施例1のN
o.1〜6と各々同配合及び同焼成条件にて粒状体を製
造し、同様に特性試験を行ったところ、いずれの場合
も、実施例1で得られた粒状体とほぼ同等の平均粒径、
圧潰強度、非溶出性、一軸圧縮強度、修正CBRを示す
粒状体が得られた。
N in Example 1 except that municipal waste and / or water-treated sludge (dry product) was previously crushed by a mill to an average particle size of 50 μ and then mixed with limestone having an average particle size of 50 μ.
o. Granules were produced under the same composition and firing conditions as those of Nos. 1 to 6, respectively, and characteristic tests were conducted in the same manner. In each case, an average particle diameter almost equal to that of the granules obtained in Example 1,
Granules were obtained that exhibited crush strength, non-dissolution, uniaxial compression strength, and modified CBR.

【0039】[0039]

【発明の効果】以上詳述した通り、本発明の廃棄物より
製造した粒状物及び廃棄物処理方法によれば、都市ゴミ
や水処理汚泥から、コンクリート骨材、路盤材、埋め戻
し材等として有用な粒状体を容易かつ効率的に、安価に
得ることができる。
As described above in detail, according to the granular material and the waste treatment method produced from the waste of the present invention, it can be used as concrete aggregate, roadbed material, backfill material, etc. from municipal waste and water treatment sludge. Useful granules can be obtained easily, efficiently and inexpensively.

【0040】本発明の廃棄物より製造した粒状物及び廃
棄物処理方法は廃棄物の減量化及び有効再利用に有効で
あり、省資源のための技術としてその工業的、社会的有
用性は極めて大である。
The particulate matter produced from waste and the method for treating waste according to the present invention are effective in reducing the amount of waste and effectively reusing it, and its industrial and social utility is extremely useful as a resource-saving technique. Is large.

───────────────────────────────────────────────────── 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 B09B 3/00 303 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical indication C04B 18/10 Z B09B 3/00 303

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 都市ゴミ及び/又は水処理汚泥と石灰石
とを混合粉砕した後、回転式焼成炉にて1000〜15
00℃で焼成して得られる、粒径40mm以下の焼き締
まった粒状体よりなる廃棄物より製造した粒状物。
1. Municipal waste and / or water treatment sludge and limestone are mixed and pulverized, and then 1000 to 15 in a rotary firing furnace.
Granules produced from waste consisting of compacted granules with a particle size of 40 mm or less, obtained by firing at 00 ° C.
【請求項2】 都市ゴミ及び/又は水処理汚泥と石灰石
とを各々粉砕した後混合し、次いで、回転式焼成炉にて
1000〜1500℃で焼成して得られる、粒径40m
m以下の焼き締まった粒状体よりなる廃棄物より製造し
た粒状物。
2. Municipal waste and / or water-treated sludge and limestone are crushed and mixed, respectively, and then calcinated in a rotary calcination furnace at 1000 to 1500 ° C. to obtain a particle size of 40 m.
Granules produced from waste consisting of compacted granules of m or less.
【請求項3】 都市ゴミ及び/又は水処理汚泥と石灰石
とを混合粉砕した後、回転式焼成炉にて1000〜15
00℃で焼成し、粒径40mm以下の焼き締まった粒状
体とすることを特徴とする廃棄物処理方法。
3. Municipal waste and / or water treatment sludge and limestone are mixed and pulverized, and then 1000 to 15 in a rotary firing furnace.
A method for treating waste, which comprises firing at 00 ° C. to obtain a compacted particle having a particle size of 40 mm or less.
【請求項4】 都市ゴミ及び/又は水処理汚泥と石灰石
とを各々粉砕した後混合し、次いで、回転式焼成炉にて
1000〜1500℃で焼成し、粒径40mm以下の焼
き締まった粒状体とすることを特徴とする廃棄物処理方
法。
4. Municipal waste and / or water-treated sludge and limestone are crushed and mixed together, and then calcinated in a rotary calcination furnace at 1000 to 1500 ° C. A waste treatment method characterized by the following.
JP11512594A 1994-05-27 1994-05-27 Waste treatment method Expired - Fee Related JP3261601B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11512594A JP3261601B2 (en) 1994-05-27 1994-05-27 Waste treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11512594A JP3261601B2 (en) 1994-05-27 1994-05-27 Waste treatment method

Publications (2)

Publication Number Publication Date
JPH07313950A true JPH07313950A (en) 1995-12-05
JP3261601B2 JP3261601B2 (en) 2002-03-04

Family

ID=14654891

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11512594A Expired - Fee Related JP3261601B2 (en) 1994-05-27 1994-05-27 Waste treatment method

Country Status (1)

Country Link
JP (1) JP3261601B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020000613A (en) * 2000-06-26 2002-01-05 이상수 Ascon manufacturing method with abandoned

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020000613A (en) * 2000-06-26 2002-01-05 이상수 Ascon manufacturing method with abandoned

Also Published As

Publication number Publication date
JP3261601B2 (en) 2002-03-04

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