JP2006016217A - General waste incineration ash regenerated aggregate and its production method - Google Patents

General waste incineration ash regenerated aggregate and its production method Download PDF

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JP2006016217A
JP2006016217A JP2004192610A JP2004192610A JP2006016217A JP 2006016217 A JP2006016217 A JP 2006016217A JP 2004192610 A JP2004192610 A JP 2004192610A JP 2004192610 A JP2004192610 A JP 2004192610A JP 2006016217 A JP2006016217 A JP 2006016217A
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incineration ash
waste incineration
general waste
particle size
aggregate
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Toshihiko Takagi
利彦 高木
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Lay Corp
LAY Corp KK
Nikko Co Ltd
Nikko KK
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Lay Corp
LAY Corp KK
Nikko Co Ltd
Nikko KK
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    • 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

Abstract

<P>PROBLEM TO BE SOLVED: To solve the problem that, regarding the conventional regenerating method for general waste incineration ash, the application of regenerated products has been limited to specified purposes such as civil engineering materials, and the consumption demand in an amount corresponding to that of the regenerated products has not been expected, thus the surplus products must be carried into final disposal places after all. <P>SOLUTION: General waste incineration ash is sorted and classified by prescribed grain size by a grain size sorting screen 18, and is coated with cement and lime fine powder using a formalin condensate admixture of melamine sulfonate, so as to be formed into concrete aggregate for a secondary product to which a lot of consumption demand is expected. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は一般廃棄物焼却灰を土木資材や2次製品用コンクリートの骨材に再生した一般廃棄物焼却灰再生骨材とその製造方法に関するものである。   The present invention relates to a general waste incinerated ash recycled aggregate obtained by regenerating general waste incinerated ash into an aggregate of civil engineering materials or concrete for secondary products, and a method for producing the same.

現在、国内では年間約5000万トンの一般廃棄物が発生し、約4000万トンが焼却処理され、これに伴って約600万トンの焼却灰が発生しているが、このうち再生して資源化されているのは10万トン程度で残りは最終処分場に持ち込まれている。   Currently, about 50 million tons of general waste is generated annually in Japan, and about 40 million tons are incinerated, resulting in about 6 million tons of incineration ash. About 100,000 tons have been converted to the final disposal site.

従来、一般廃棄物焼却灰の再生方法として提案されているものとしては、一般廃棄物焼却灰に、石膏を含有する高炉水砕微粉末を水とともに添加・混合し、その混合物を押し出し成形機器にて成形する方法(例えば特許文献1参照)が開発されている。   Conventionally, as a method for regenerating general waste incineration ash, blast furnace granulated fine powder containing gypsum is added to and mixed with general waste incineration ash together with water, and the mixture is used as an extrusion molding machine. A method for forming the mold (for example, see Patent Document 1) has been developed.

また、一般廃棄物焼却灰を脱硫スラッジ或いは脱硫スラッジと石炭灰との混合物によって一般廃棄物焼却灰に含有される鉛を封じ込める方法(例えば特許文献2参照)が提案されている。
特開平9ー174019号公報 特開平10ー277516号公報
Further, a method has been proposed in which lead contained in general waste incineration ash is contained in general waste incineration ash by desulfurization sludge or a mixture of desulfurization sludge and coal ash (see, for example, Patent Document 2).
Japanese Patent Laid-Open No. 9-174019 JP-A-10-277516

しかしながら、一般廃棄物焼却灰に石膏を含有する高炉水砕微粉末を水とともに添加・混合し、その混合物を押し出し成形する方法は、焼却灰中の重金属溶出を完全に封鎖する効果までは期待できず、高炉水砕微粉末自体に有害物質が含有されているため、その溶出を防止するため混合物の押出成形手段を採っていて大規模な処理プラントの建設を必要とする等の問題がある。   However, the method of adding and mixing blast furnace granulated fine powder containing gypsum with incinerated ash to general waste incinerated ash and extruding the mixture can be expected to completely block the elution of heavy metals in the incinerated ash. However, since the blast furnace granulated fine powder itself contains harmful substances, there is a problem that it is necessary to construct a large-scale processing plant by adopting a means for extrusion of the mixture in order to prevent elution.

また、脱硫スラッジ或いは脱硫スラッジと石炭灰との混合物によって一般廃棄物焼却灰に含有される鉛を封じ込める方法は、脱硫スラッジ自体が産業廃棄物で特殊な処理を必要とし封鎖重金属も鉛に限定される問題がある。   In addition, the method of containing lead contained in municipal waste incineration ash with desulfurization sludge or a mixture of desulfurization sludge and coal ash requires that the desulfurization sludge itself is an industrial waste and requires special treatment, and the heavy metals sealed are also limited to lead. There is a problem.

これら従来の一般廃棄物焼却灰の再生方法について更に問題なのは、再生される産出物の用途が土木材料等の特定目的に限定され、再生される産出物の量に対応する量の消費需要が見込まれないため、余剰産出物は結局最終処分場に持ち込まれざるを得ないことにある。   A further problem with these conventional waste incineration ash recycling methods is that the use of recycled products is limited to specific purposes, such as civil engineering materials, and demand for consumption corresponding to the amount of recycled products is expected. As a result, surplus products are eventually brought to the final disposal site.

更に、従来の処理方法は、処理プラントの建設に極めて高額な費用が必要なため、これに見合う一般廃棄物焼却灰の大量処理を行わなければ採算がとれず、焼却灰の発生は場所的に分散しているため採算がとれるだけの大量の一般廃棄物焼却灰を集荷するためには焼却灰の長距離移動が必要となり、運搬費によるコスト高額化や移動沿線における公害等による住民の反対も問題となる。   Furthermore, the conventional treatment method requires a very high cost for the construction of the treatment plant, so it cannot be profitable unless a large amount of municipal waste incineration ash is processed in proportion to this, and the generation of incineration ash is local. In order to collect a large amount of municipal waste incineration ash that can be profitable because it is dispersed, it is necessary to move the incineration ash over a long distance, and the opposition of residents due to high costs due to transportation costs and pollution along the movement It becomes a problem.

本発明は、上記の課題に対応してこれを解決するため、一般廃棄物焼却灰を粒径によって選別区分し、メラミンスルホン酸塩のホルマリン縮合物を主成分とする混和剤を用いてセメントと石灰石微粉末によりコーティングすることにより、重金属溶出を封鎖して再生骨材として使用できるように構成した。   In order to solve the above-mentioned problems, the present invention sorts municipal waste incineration ash according to particle size, and uses an admixture mainly composed of a formalin condensate of melamine sulfonate and cement. By coating with limestone fine powder, heavy metal elution was sealed off and used as recycled aggregate.

即ち、メラミンスルホン酸塩のホルマリン縮合物は、一定粒径の一般廃棄物焼却灰とコーティング材となるセメント及び石灰石微粉末との馴染みを無理なく促進し、コーティング材と焼却灰骨材との分離を防止する作用があるので、これを利用して重金属溶出を封鎖するようにしたものである。   In other words, the formalin condensate of melamine sulfonate facilitates the familiarization of the general waste incineration ash with a fixed particle size with the cement and limestone fine powder used as the coating material, thereby separating the coating material from the incinerated ash aggregate. This is used to block heavy metal elution.

また、コーティングの方法としてメラミンスルホン酸塩のホルマリン縮合物を水との混和水溶液に構成して、一定粒径毎に選別区分した廃棄物焼却灰に噴霧して加湿するようにして、コーティング環境の調整と計測された廃棄物焼却灰の含水比との調整を図った配合設計を行えるようにし、ミキサーによるセメント及び石灰石微粉末との機械的な混合で適切なコーティングが行えるようにした。   In addition, as a coating method, a formalin condensate of melamine sulfonate is formed into an aqueous solution mixed with water and sprayed onto waste incinerated ash that is sorted according to a certain particle size to humidify the coating environment. The blending design was adjusted so that the adjustment and the moisture content of the measured waste incineration ash were adjusted, and appropriate mixing could be performed by mechanical mixing with cement and fine limestone powder by a mixer.

更に、一般廃棄物焼却灰の粒径を5ミリ以下と、5ミリより大きく10ミリ以下のもの、10ミリより大きく15ミリ以下のものに区分選別するようにして、分散した工事現場でなく集中した大量の消費需要が見込まれる工場加工における資材としての2次製品用コンクリート骨材に生成し、処理再生品を一挙に需要現場に供給して余剰再生品の発生を抑制し、処理再生品の利用が促進されるようにした。   Furthermore, the particle size of general waste incineration ash is classified into 5 mm or less, more than 5 mm and less than 10 mm, more than 10 mm and less than 15 mm, and concentrated instead of dispersed construction sites. Generated into concrete aggregates for secondary products as materials in factory processing where a large amount of consumer demand is expected, and processed recycled products are supplied to the demand site at once to suppress the generation of surplus recycled products. The use was promoted.

このように、処理再生品を工場加工製品の原材料に再生することにより、一般廃棄物焼却灰処理プラントとコンクリート2次製品プラントとの連携により、処理再生品の合理的利用が促進されるものである。   In this way, by reusing treated recycled products as raw materials for factory processed products, rational use of treated recycled products is promoted through cooperation between the municipal waste incineration ash treatment plant and the concrete secondary product plant. is there.

以下図面と処理の流れに従って本発明の実施の形態を説明する。1は受材ホッパーで、集荷トラックAから一般廃棄物焼却灰原料をバイブレーター付傾斜グリズリ11を介して投入を受け、異物を除去する磁選機12を設けた引出しベルトコンベヤ2上に供給する。処理量としては1バッチ300リットル(187.5kg)程度としてモータープーリー低速型ベルトコンベヤによってフロー処理される。   Embodiments of the present invention will be described below with reference to the drawings and the flow of processing. Reference numeral 1 denotes a receiving hopper, which receives the general waste incinerated ash raw material from the collection truck A through an inclined grizzly ring 11 with a vibrator, and supplies it onto a draw-out belt conveyor 2 provided with a magnetic separator 12 for removing foreign matter. The processing amount is about 300 liters (187.5 kg) per batch, and the flow is processed by a motor pulley low speed belt conveyor.

磁選機12は吊下げ式自動排出型で、下部の引出しベルトコンベヤ2によって搬送される焼却灰原料中に混入されている陶器・ガラスの破片、鉄くず、釘等の異物をを磁選により選別して自動的に排出し、純粋な焼却灰として粒径選別スクリーン13に供給する。   The magnetic separator 12 is a suspension type automatic discharge type, and it sorts out foreign substances such as ceramics, glass fragments, iron scraps and nails mixed in the incinerated ash raw material conveyed by the lower drawer belt conveyor 2 by magnetic separation. Are automatically discharged and supplied to the particle size sorting screen 13 as pure incineration ash.

粒径選別スクリーン13は、粒径15ミリ以下の原料を透過するスクリーン、粒径10ミリ以下の原料を透過するスクリーン、粒径5ミリ以下の原料を透過するスクリーンの3層に設定され、粒径を5ミリ以下と、5ミリより大きく10ミリ以下のもの、10ミリより大きく15ミリ以下のもの、15ミリ以上のものに分別されて、それぞれのスクリーン上に残留し、貯蔵槽への搬送ベルト21、22、23により各粒径毎の3つの分別貯蔵槽15、16、17に搬送され、15ミリ以上のものはオーバーサイズヤード14に搬出される。   The particle size selection screen 13 is set in three layers: a screen that transmits a raw material with a particle size of 15 mm or less, a screen that transmits a raw material with a particle size of 10 mm or less, and a screen that transmits a raw material with a particle size of 5 mm or less. Separated into diameters of 5 mm or less, 5 mm or more and 10 mm or less, 10 mm or more and 15 mm or less, or 15 mm or more, and remaining on each screen, transported to storage tank The belts 21, 22, 23 are transported to three separate storage tanks 15, 16, 17 for each particle size, and those of 15 mm or more are transported to the oversize yard 14.

3つの分別貯蔵槽に搬送貯留された分別原料は、その下部に設定された計量ベルト24、25、26を通じて各区分粒径毎に順次コーティングミキサー18に投入される。ミキサー18の基台部には計量ロ−ドセル19が付設され投入された分別原料を計量して分別原料投入量に対応した個別配合設計が行われるようになっている。   The separated raw materials conveyed and stored in the three separate storage tanks are sequentially fed into the coating mixer 18 for each divided particle size through the measuring belts 24, 25, 26 set in the lower part thereof. A metering load cell 19 is attached to the base portion of the mixer 18 to measure the fractionated raw material that has been input, and an individual blending design corresponding to the amount of fractional raw material input is performed.

基本的な配合設計としては、一般廃棄物焼却灰300kgに対して、水28kg、混和剤2kg、ポルトランドセメント5kg、石灰石微粉末1kg程度で粒径やコーティング環境によって設計され計算される。   As a basic blending design, 28 kg of water, 2 kg of admixture, 5 kg of Portland cement, and 1 kg of fine limestone powder are designed and calculated according to the particle size and coating environment for 300 kg of general waste incineration ash.

コーティングミキサー18に投入された分別原料は、混和剤としてのメラミンスルホン酸塩のホルマリン縮合物と水との混和水溶液の噴霧を受けて加湿されるのであるが、この水溶液は混和剤タンク3と清水タンク31からそれぞれに付設された計量ポンプP1、P2によって計量調整されながら混合槽32に供給される混和剤と水とによって混合槽32内において混和水溶液が調製される。   The fractionated raw material charged in the coating mixer 18 is sprayed with an aqueous mixture of melamine sulfonate formalin condensate as an admixture and water and is humidified. This aqueous solution is mixed with the admixture tank 3 and fresh water. A mixed aqueous solution is prepared in the mixing tank 32 by the admixture and water supplied from the tank 31 to the mixing tank 32 while being metered by the metering pumps P1 and P2 attached thereto.

調製された混和水溶液は、加圧タンク33に送られて加圧され扇状噴霧ノズル34を通じてコーティングミキサー18内で回動する分別原料に噴霧され、コーティング環境に適応する加湿条件をもって分別原料を加湿する。   The prepared mixed aqueous solution is sent to the pressurizing tank 33, pressurized, sprayed onto the separation raw material rotating in the coating mixer 18 through the fan spray nozzle 34, and humidifies the separation raw material under humidification conditions suitable for the coating environment. .

噴霧加湿は、水28kgに対して混和剤2kg程度を投入した水溶液を、毎分8.17リッターの吐出量、2kg/平方センチの吐出圧をもって噴射することによって行われる。   Spray humidification is performed by injecting an aqueous solution in which about 2 kg of admixture is added to 28 kg of water with a discharge amount of 8.17 liters per minute and a discharge pressure of 2 kg / square centimeter.

分別原料に対する加湿を終わった段階で、コーティング材であるセメント及び石灰石微粉末がセメントタンク4と石灰石微粉末タンク41から、それぞれの計量槽42、43によって計量されながら配合設計に対応してミキサー18に投入され、ミキサーの回動によって混合されることによって分別原料に対するコーティングが行われる。   At the stage where the humidification of the separated raw materials is finished, the cement and limestone fine powder, which are coating materials, are measured from the cement tank 4 and the limestone fine powder tank 41 by the respective measuring tanks 42 and 43, corresponding to the blending design. The raw material is coated on the fractionated raw material by mixing by turning the mixer.

コーティングが完了すると、コーティングされた分別原料はインバーター付ベルトフィーダーを付設した定量供給ホッパー44に搬入され、ドライヤー45を通して乾燥仕上げを行ったうえホットベルトコンベヤ46によって分別貯蔵槽47、48、49に搬送して区分粒径毎に貯蔵される。   When coating is completed, the coated fractionated raw material is carried into a quantitative feed hopper 44 equipped with a belt feeder with an inverter, dried through a dryer 45, and then transported to a fractionation storage tank 47, 48, 49 by a hot belt conveyor 46. And stored for each segment particle size.

ドライヤー45は、送入口側に設定されたバーナー5が重油タンク51からの燃料供給によってドライヤー内に熱風を吹き込み、塵埃と熱風を集塵機52を介した排風機53により吸引してドライヤー内を通過するコーティング分別原料を熱風乾燥するようになっている。ドライヤー内の加熱温度は50〜75度C程度である。   In the dryer 45, the burner 5 set on the inlet side blows hot air into the dryer by supplying fuel from the heavy oil tank 51, and the dust and hot air are sucked by the blower 53 through the dust collector 52 and pass through the dryer. The coating separation raw material is dried with hot air. The heating temperature in the dryer is about 50 to 75 degrees C.

以上の工程は各区分粒径分別原料毎に順次行っていくか、区分粒径分別後の加工経路を3セット設定し、区分粒径別のセットによって同時進行させる方法によって行う。   The above steps are sequentially performed for each classified particle size sorting raw material, or are performed by a method in which three sets of processing paths after the classified particle size classification are set and are simultaneously advanced by the set for each classified particle size.

このような加工処理によって生成された再生骨材は、粒径5ミリ以下のものは砂の代替骨材として、5ミリより大きく10ミリ以下のもの、10ミリより大きく15ミリ以下のものは、砂礫或いは砕石の代替骨材として2次製品用コンクリート骨材として用いることができる。   Recycled aggregates produced by such processing are those having a particle size of 5 mm or less as substitute aggregates for sand, those having a size larger than 5 mm but not larger than 10 mm, those having a particle size larger than 10 mm and not larger than 15 mm, It can be used as a concrete aggregate for secondary products as an alternative aggregate for gravel or crushed stone.

一般廃棄物焼却灰は見掛け比重1で、含水比20%程度の原料であり、福井県武生市の一般廃棄物焼却施設において発生した一般廃棄物焼却灰についてふるい分け試験を行った結果は、粒度分布は粒径5ミリ以下のもの71.60%、5ミリより大きく10ミリ以下のものは16.30%、10ミリより大きく15ミリ以下のものは6.30%、15ミリ以上のものは5.80%であった。粒径15ミリ以上のものを廃棄したとしても再生率は可なり高いものとなる。   General waste incineration ash is a raw material with an apparent specific gravity of 1 and a water content of about 20%. The results of a screening test on general waste incineration ash generated at a general waste incineration facility in Takefu City, Fukui Prefecture show the particle size distribution. The particle size is 71.60% for particles of 5 mm or less, 16.30% for particles greater than 5 mm and 10 mm or less, 6.30% for particles greater than 10 mm and 15 mm or less, and 5 for particles larger than 15 mm. 80%. Even if the particles having a particle diameter of 15 mm or more are discarded, the regeneration rate is considerably high.

出願人は、以上のように処理加工された再生骨材を用いて成形したコンクリート2次製品について、カンタブ測定器(小野田セメント製)により塩化物測定を行なった結果、塩素濃度の平均値は0.0061%、単位水量は199kg/立方メートル、塩化物質は0.1299kg/立方メートルであって基準内の結果を得ることができた。   As a result of the chloride measurement by the cantab measuring instrument (manufactured by Onoda Cement), the applicant determined that the average value of the chlorine concentration was 0 for the concrete secondary product molded using the recycled aggregate processed and processed as described above. .0061%, the unit water amount was 199 kg / cubic meter, the chlorinated substance was 0.1299 kg / cubic meter, and the result within the standard could be obtained.

コンクリート2次製品加工前の再生骨材のフロー値は最大590ミリ、最小585ミリで、空気量2.3%、塩化物イオン量0.129kg/立方メートルである。   The flow value of the recycled aggregate before processing the secondary concrete product is 590 mm at the maximum and 585 mm at the minimum, the air amount is 2.3%, and the chloride ion amount is 0.129 kg / cubic meter.

また、再生骨材を用いて成形したコンクリート2次製品の強度試験結果は、成形後2日で平均25.1ニュートン/平方ミリ、7日で平均36.8ニュートン/平方ミリという結果を得ることができた。   In addition, the strength test results of secondary concrete products molded using recycled aggregates should yield an average of 25.1 newtons / square millimeter 2 days after molding and an average of 36.8 newtons / square millimeter after 7 days. I was able to.

更に、重量及び容積について行なった試験では、成形後2日で重量は平均3558.0g、容積は平均1549.8立方センチ、成形後7日で重量は平均3514.1g、容積は平均1550.9立方センチであった。   Further, in tests conducted on weight and volume, the average weight was 3558.0 g and the volume was 1549.8 cubic centimeters two days after molding, and the average weight was 3514.1 g and the volume was average 1550.9 g seven days after molding. It was cubic centimeter.

本発明は以上のように構成したので、一般廃棄物焼却灰とセメント及び石灰石微粉末との馴染みを無理なく促進し、焼却灰骨材との分離を防止するメラミンスルホン酸塩のホルマリン縮合物を水溶液として、廃棄物焼却灰に噴霧し適切な加湿状態としてコーティングすることにより、一般廃棄物焼却灰を安定した再生骨材として生成できたものである。   Since the present invention is configured as described above, a formalin condensate of melamine sulfonate that facilitates the familiarization of general waste incinerated ash with cement and fine limestone powder and prevents separation from the incinerated ash aggregate is provided. By spraying the waste incineration ash as an aqueous solution and coating it in an appropriate humidified state, the general waste incineration ash can be produced as a stable recycled aggregate.

また、消費需要率の高い一般廃棄物焼却灰をコンクリート2次製品の再生骨材に生成することにより、コンクリート2次製品成形工場が一般廃棄物焼却灰処理プラントを付設して成形に必要な骨材を焼却灰処理を行いながら生産でき、過剰再生による無駄をなくして一般廃棄物焼却灰の処理による再生産出物と再生産出物に対する消費需要とのバランスを図ることができるものである。   In addition, by generating municipal waste incineration ash with a high consumption demand rate into recycled aggregates of concrete secondary products, the concrete secondary product molding plant is equipped with a general waste incineration ash treatment plant to provide the necessary bones for molding. The material can be produced while incineration ash processing is performed, and waste due to excessive regeneration can be eliminated, and the balance between the regenerated output by the general waste incineration ash process and the consumption demand for the regenerated output can be achieved.

本発明の実施例による処理工程を示すもので、一般廃棄物焼却灰原料から異物を除去し粒径区分を行って区分槽に選別貯留するまでのフローシステムを示す装置の全体側面図The processing apparatus by the Example of this invention is shown, The whole side view of the apparatus which shows the flow system until it removes a foreign material from a general waste incineration ash raw material, performs a particle size division, and is sorted and stored in a division tank 同じく、加湿混和水溶液の生成とコーティングミキサーへの噴霧供給フローシステムを示す装置の全体側面図Similarly, an overall side view of the apparatus showing the generation of the humidified aqueous mixture and the spray supply flow system to the coating mixer 同じく、コーティングミキサーへの処理原料供給とコーティング処理からドライヤーへの搬送フローシステムを示す装置の全体側面図Similarly, the entire side view of the equipment showing the processing raw material supply to the coating mixer and the transport flow system from the coating process to the dryer 同じく、ドライヤーでの乾燥処理システムと産出再生骨材の粒径区分槽への搬送フローシステムを示す装置の全体側面図Similarly, an overall side view of the apparatus showing a drying treatment system with a dryer and a flow system for transporting the output recycled aggregate to the particle size division tank

符号の説明Explanation of symbols

1 受材ホッパー
11 バイブレーター付傾斜グリズリ
12 異物を除去する磁選機
13 粒径選別スクリーン
14 オーバーサイズヤード
15 分別貯蔵槽
16 分別貯蔵槽
17 分別貯蔵槽
18 コーティングミキサー
19 計量ロ−ドセル
2 引出しベルトコンベヤ
21 貯蔵槽への搬送ベルト
22 貯蔵槽への搬送ベルト
23 貯蔵槽への搬送ベルト
24 計量ベルト
25 計量ベルト
26 計量ベルト
3 混和剤タンク
31 清水タンク
32 混合槽
33 加圧タンク
34 扇状噴霧ノズル
4 セメントタンク
41 石灰石微粉末タンク
42 セメントタンクの計量槽
43 石灰石微粉末タンクの計量槽
44 コーティングされた分別原料の定量供給ホッパー
45 ドライヤー
46 ホットベルトコンベヤ
47 乾燥処理された再生骨材の分別貯蔵槽
48 乾燥処理された再生骨材の分別貯蔵槽
49 乾燥処理された再生骨材の分別貯蔵槽
5 乾燥バーナー
51 重油タンク
52 集塵機
53 排風機
A 集荷トラック
B 出荷トラック
P 計量ポンプ
a エアバイブレーター
DESCRIPTION OF SYMBOLS 1 Receipt hopper 11 Inclined grizzle with vibrator 12 Magnetic separator which removes foreign substances 13 Grain size selection screen 14 Oversize yard 15 Sort storage tank 16 Sort storage tank 17 Sort storage tank 18 Coating mixer 19 Weighing load cell 2 Drawer belt conveyor 21 Conveying belt to storage tank 22 Conveying belt to storage tank 23 Conveying belt to storage tank 24 Measuring belt 25 Measuring belt 26 Measuring belt 3 Admixture tank 31 Fresh water tank 32 Mixing tank 33 Pressurizing tank 34 Fan-shaped spray nozzle 4 Cement tank 41 Limestone fine powder tank 42 Cement tank weighing tank 43 Limestone fine powder tank weighing tank 44 Quantitative supply hopper for coated separated raw materials 45 Dryer 46 Hot belt conveyor 47 Sorted storage tank for dried recycled aggregate 4 Drying the treated recycled aggregate fractional reservoir 49 Drying the treated regeneration aggregate fractional storage tank 5 dry burners 51 fuel oil tank 52 dust collector 53 exhaust fan A collection truck B ship track P metering pump a air vibrator

Claims (3)

一般廃棄物焼却灰を粒径によって選別区分し、メラミンスルホン酸塩のホルマリン縮合物を主成分とする混和剤を用いてセメントと石灰石微粉末によりコーティングしたことを特徴とする一般廃棄物焼却灰再生骨材   General waste incineration ash recycle characterized by being classified and classified according to particle size and coated with cement and limestone fine powder using an admixture based on formalin condensate of melamine sulfonate aggregate 粒径を5ミリ以下と、5ミリより大きく10ミリ以下のもの、10ミリより大きく15ミリ以下のものに区分選別するようにして2次製品用コンクリート骨材に生成した請求項1記載の一般廃棄物焼却灰再生骨材 2. The general aggregate according to claim 1, wherein the particle size is classified into 5 mm or less, greater than 5 mm and less than 10 mm, and more than 10 mm and less than 15 mm, and produced into concrete aggregate for secondary products. Waste incineration ash recycled aggregate 異物を除去し、粒径によって選別区分した一般廃棄物焼却灰を、メラミンスルホン酸塩のホルマリン縮合物を主成分とする混和水溶液によって噴霧加湿し、ミキサーによってセメント及び石灰石微粉末と混合することによってコーティングした上で乾燥することを特徴とする一般廃棄物焼却灰再生骨材の製造方法
By spraying and humidifying general waste incineration ash, which is free from foreign substances, and sorted according to particle size, with a mixed aqueous solution composed mainly of a formalin condensate of melamine sulfonate, and mixed with cement and fine limestone powder by a mixer A method for producing general waste incinerated ash recycled aggregate characterized by drying after coating
JP2004192610A 2004-06-30 2004-06-30 General waste incineration ash regenerated aggregate and its production method Pending JP2006016217A (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104028528A (en) * 2013-03-04 2014-09-10 上海科锐驰化工装备技术有限公司 Solidification apparatus for fly ash produced in power generation through burning of municipal waste
CN112275623A (en) * 2020-10-12 2021-01-29 唐山威豪镁粉有限公司 Sieve array for sieving in magnesium powder production process
CN113338260A (en) * 2021-06-18 2021-09-03 青海省交通控股集团有限公司 Construction waste recycled aggregate dry-mixed cement gravel pile and preparation method thereof
CN113564982A (en) * 2021-08-17 2021-10-29 广东德泽建设工程有限公司 Sidewalk based on construction waste recycling and construction method thereof
CN115448676A (en) * 2022-10-11 2022-12-09 南京理工大学 Fluidized bed solid sulfur ash artificial lightweight aggregate

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104028528A (en) * 2013-03-04 2014-09-10 上海科锐驰化工装备技术有限公司 Solidification apparatus for fly ash produced in power generation through burning of municipal waste
CN112275623A (en) * 2020-10-12 2021-01-29 唐山威豪镁粉有限公司 Sieve array for sieving in magnesium powder production process
CN113338260A (en) * 2021-06-18 2021-09-03 青海省交通控股集团有限公司 Construction waste recycled aggregate dry-mixed cement gravel pile and preparation method thereof
CN113564982A (en) * 2021-08-17 2021-10-29 广东德泽建设工程有限公司 Sidewalk based on construction waste recycling and construction method thereof
CN113564982B (en) * 2021-08-17 2022-06-07 广东德泽建设工程有限公司 Sidewalk based on construction waste recycling and construction method thereof
CN115448676A (en) * 2022-10-11 2022-12-09 南京理工大学 Fluidized bed solid sulfur ash artificial lightweight aggregate
CN115448676B (en) * 2022-10-11 2023-10-13 南京理工大学 Fluidized bed solid sulfur ash artificial lightweight aggregate

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