JP2012115838A - Wet sorting apparatus - Google Patents

Wet sorting apparatus Download PDF

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JP2012115838A
JP2012115838A JP2012029643A JP2012029643A JP2012115838A JP 2012115838 A JP2012115838 A JP 2012115838A JP 2012029643 A JP2012029643 A JP 2012029643A JP 2012029643 A JP2012029643 A JP 2012029643A JP 2012115838 A JP2012115838 A JP 2012115838A
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water
cleaning
tank
washing
wet
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JP5292483B2 (en
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Yasuhiro Yoshizaki
耕大 吉崎
Yuichi Yonezu
雄一 米津
Daisuke Yoshino
大輔 吉野
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Kubota Corp
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Abstract

PROBLEM TO BE SOLVED: To provide a wet sorting apparatus capable of classifying granular powders even while simplifying facilities to reduce the amount of cleaning water and capable of efficiently removing obstacles such as water-soluble components or heavy metals.SOLUTION: In a U tube-shaped cleaning tank 20 having a pulsation generator 30, a granular object to be treated is separated into a particulate and a medium particulate by utilizing the difference of sedimentation speed, an upper-layer cleaning water is drained together with the particulate from an overflow weir 26 being a drain path, and the medium particulate settled in the cleaning tank 20 is taken out of the tank by a bucket type conveyor device 29. A draining opening is formed on the bottom of a bucket, and a water-feeding nozzle is provided to spray-supply a rinse water to the object after draining.

Description

本発明は、粗大物等が混入した粉粒状の処理対象物を洗浄して該処理対象物に混入する障害物質を除去する湿式選別装置に関する。   The present invention relates to a wet sorting apparatus that cleans a granular processing object mixed with a coarse material and the like and removes obstacle substances mixed in the processing object.

金属類、ガラ類(石やガラス片等)さらには有機質材(ゴム、プラスチック、紙、繊維、木片等)といった粗大物が混入した灰や土壌等の粉粒体を資源化して再利用する場合、粗大物を分離除去するとともに資源化に障害となる様々な水溶性成分や重金属等の障害物質を除去する必要がある。   When resources such as ash and soil mixed with metal, glass (stones, glass pieces, etc.) and organic materials (rubber, plastic, paper, fiber, wood pieces, etc.) are reused. In addition, it is necessary to separate and remove coarse substances and to remove various water-soluble components and heavy substances such as heavy metals that impede resource recycling.

例えば、一般に都市ゴミ焼却施設等で発生した焼却灰等の焼却残渣をセメント原料として再利用する場合には、焼却残渣から金属類、ガラ類、有機質材等の粗大物を分離除去するとともに、焼却灰に付着した塩分等を除去する必要がある。   For example, when incineration residue such as incineration ash generated at municipal waste incineration facilities is reused as a raw material for cement, coarse materials such as metals, glass and organic materials are separated and removed from the incineration residue and incinerated. It is necessary to remove salt attached to the ash.

また、雑多な廃棄物が不法投棄された汚染土壌を浄化して再利用する場合には、土壌を掘削して金属類、ガラ類、有機質材等の粗大物を分離除去するとともに、土砂に付着した重金属等の有害成分を除去する必要がある。   In addition, when purifying and reusing contaminated soil in which miscellaneous waste has been illegally dumped, the soil is excavated to separate and remove coarse materials such as metals, glass, and organic materials, and adhere to soil and sand. It is necessary to remove harmful components such as heavy metals.

従来からこのような処理対象物に対しては、磁選機や振動篩で粗大物を除去した後に、粉粒体を水で洗浄する方法が採用されていたが、処理対象物の含水量が多いと金属類に粉粒体が付着するために磁選機で良好に選別できず、振動篩の篩目が有機質材で閉塞されるために頻繁にメンテナンスが必要になるといった問題があり、また、選別された粗大物に付着した粉粒体を別工程で洗浄しなければならず、設備が増えるばかりか、洗浄のための水量が増し、洗浄装置の後段に大型の排水処理設備を設置しなければならないという問題があった。   Conventionally, for such a processing object, a method of washing the granular material with water after removing coarse material with a magnetic separator or a vibrating sieve has been adopted, but the water content of the processing object is large. In addition, the powder particles adhere to the metal and cannot be sorted well with a magnetic separator, and the mesh of the vibrating sieve is clogged with organic materials, so frequent maintenance is required. In addition to increasing the number of facilities, the amount of water used for cleaning must be increased, and a large wastewater treatment facility must be installed after the cleaning device. There was a problem of not becoming.

そこで、特許文献1には、都市ごみ焼却灰中からステンレス等の異物と、含まれる塩素分とを同時に除去することを目的として、水槽内の水中に保持された都市ごみ焼却灰を上下に躍動させて、この都市ごみ焼却灰中の塩素分を水洗すると同時に、比重の差を利用した比重選別により、この都市ごみ焼却灰のうち、比較的比重の小さい灰成分を分離する一方、比較的比重の大きな金属類成分を除去する都市ごみ焼却灰の塩素及び金属類等の除去方法が提案されている。   Therefore, in Patent Document 1, the municipal waste incineration ash held in the water in the aquarium is moved up and down for the purpose of simultaneously removing foreign substances such as stainless steel and contained chlorine from the municipal waste incineration ash. The municipal waste incineration ash was washed with water, and at the same time, the ash components having a relatively low specific gravity were separated from the municipal waste incineration ash by specific gravity selection using the difference in specific gravity, while the relative specific gravity was relatively high. A method for removing chlorine, metals, etc. from municipal waste incineration ash that removes large metal components is proposed.

また、特許文献2には、焼却灰から粗粒子と微粒子を速やかに分離し、微粒子には充分に時間と適当な攪拌を与えて脱塩作用を完結させる灰の洗浄処理方法として、2段以上の複数の機械式湿式分級機を直列に設置し、前段の分級機に焼却灰を入れ後段の分級機に洗浄水を加えて洗浄脱水作用と粒子分級作用をしながら、焼却灰は前段から後段へ水は後段から前段へ向流的に接触移動させ、粗粒の焼却灰は後段から系外に取り出し、微粒の焼却灰を含んだ洗浄液は前段から取り出し、その後、洗浄液と微粒とを分離させ脱塩された焼却灰と含塩洗浄液を得る灰の洗浄処理方法が提案されている。
特開平11−90408号公報 特開2003−80199号公報
Further, Patent Document 2 discloses two or more stages as an ash washing method in which coarse particles and fine particles are quickly separated from incinerated ash, and the fine particles are given sufficient time and appropriate stirring to complete the desalting action. A series of mechanical wet classifiers are installed in series, incinerated ash is put into the former classifier, washing water is added to the latter classifier, and washing dehydration and particle classification are performed. Water is moved counter-currently from the latter stage to the former stage, coarse incineration ash is taken out of the system from the latter stage, cleaning liquid containing fine incineration ash is taken out from the previous stage, and then the washing liquid and fine particles are separated. A ash cleaning method for obtaining desalted incineration ash and a salt-containing cleaning solution has been proposed.
Japanese Patent Laid-Open No. 11-90408 JP 2003-80199 A

しかし、特許文献2に記載されているように、様々な粒径分布を有する焼却灰や土壌では、粒径によって塩類や重金属等の障害物質の汚染濃度が異なるため、同一の水槽内で均一に洗浄するのは極めて困難である。 However, as described in Patent Document 2, incinerated ash and soil having various particle size distributions, the contamination concentration of obstacle substances such as salts and heavy metals varies depending on the particle size, so that they are uniformly in the same water tank. It is extremely difficult to clean.

粉粒状の処理対象物に混入する障害物質の含有量は、粒径が小さいほど多いという傾向があり、粒径の小さなものと大きなものとを分離して洗浄した方が効率的なためである。 The content of the fault substance mixed in the processing object particulate, there is a tendency that many smaller the particle size, it was cleaned by separating the large as the particle size of the smaller ones are for efficient .

本発明は上述した問題点に鑑み、設備を簡素化して洗浄水量を低減しながらも、粉粒体を分級して、水溶性成分や重金属等の障害物質を効率的に除去することができる湿式選別装置を提供することを目的とする。 In view of the above-mentioned problems, the present invention simplifies the equipment and reduces the amount of washing water, but also classifies the granular material to efficiently remove obstacle substances such as water-soluble components and heavy metals. An object is to provide a sorting device.

上述の目的を達成するため、本発明による湿式選別装置の第一の特徴構成は、特許請求の範囲の書類の請求項1に記載した通り、洗浄槽に投入された処理対象物を洗浄水で洗浄しながら沈降速度差によって微粒物と微粒物より粒径が大きい中粒物とに分離し、分離された微粒物を上層の洗浄水とともに排水部から排出し、前記洗浄槽に沈降した中粒物をバケット式のコンベア装置により槽外に搬出するように構成された湿式選別装置であって、前記バケット式のコンベア装置のバケットの底部に水切り用の開口が形成され、水切り後の処理対象物にリンス水を噴射供給する給水ノズルを備えている点にある。 In order to achieve the above-mentioned object, the first characteristic configuration of the wet sorting apparatus according to the present invention is that, as described in claim 1 of the claims, the object to be treated put into the washing tank is washed with washing water. While washing, it is separated into fine particles and medium particles having a larger particle size than the fine particles due to the difference in settling speed, and the separated fine particles are discharged from the drainage section together with the upper washing water and settled in the washing tank. A wet-type sorting device configured to carry an object out of a tank by a bucket-type conveyor device, wherein an opening for draining is formed at the bottom of the bucket of the bucket-type conveyor device, and the processing target after draining It is in the point provided with the water supply nozzle which injects and supplies rinse water .

洗浄槽に粉粒状の処理対象物が投入されると、粉粒体は洗浄水で洗浄されながら解され、洗浄水の中を沈降していく。このとき、粒径が大きな粉粒体は粒径が小さな粉粒体より沈降速度が速いため、水面付近で浮遊する粒径が小さな粉粒体と、比較的早期に沈降する粒径が大きな粉粒体との二層に分離される。そのため、粒径が小さな粉粒体は上層の洗浄水とともに排水部から槽外に流出され、粒径が大きな粉粒体は沈降する。When the granular object to be processed is put into the cleaning tank, the granular material is dissolved while being washed with the washing water, and settles in the washing water. At this time, the powder having a large particle size has a faster settling speed than the powder having a small particle size, so that the powder having a small particle size floating near the water surface and the powder having a large particle size that settles relatively early. Separated into two layers with granules. Therefore, the granular material having a small particle size flows out of the tank together with the upper cleaning water, and the granular material having a large particle size settles.

その後、洗浄槽の底部に沈降した粒径の大きな粉粒体がバケットによって掻き揚げられ槽外に搬出される過程で、障害物質の濃度が高い洗浄水が開孔から排水されるため、粉粒体に含まれる障害物質の濃度を低減させることができる。更に、水切り後の処理対象物に給水ノズルからリンス水を噴射供給することにより、粉粒体の間隙に残存する障害物質の濃度が高い洗浄水をリンス水で置換することができ、粉粒体に含まれる障害物質の濃度をさらに低減させることができる。Then, in the process where the granular material with a large particle size that has settled at the bottom of the washing tank is lifted by the bucket and carried out of the tank, the washing water with a high concentration of the obstacle substance is drained from the opening. The concentration of the obstacle substance contained in the body can be reduced. Furthermore, by rinsing water supplied from the water supply nozzle to the object to be treated after draining, the washing water having a high concentration of an obstacle substance remaining in the gaps between the powder particles can be replaced with the rinse water. The concentration of the obstacle substance contained in can be further reduced.

同第二の特徴構成は、同請求項2に記載した通り、上述の第一の特徴構成に加えて、前記洗浄槽内の洗浄水の塩素イオン濃度または電気伝導度に基づいて、前記給水ノズルから供給されるリンス水の水量が調整される点にある。According to the second characteristic configuration, the water supply nozzle is based on the chlorine ion concentration or the electrical conductivity of the cleaning water in the cleaning tank in addition to the first characteristic configuration described above. The amount of rinse water supplied from is adjusted.

上述の構成によれば、塩素イオン濃度または電気伝導度が高いときには、リンス水の水量を増加して中粒物に含まれる塩素含有量の更なる低減を図ることができる。According to the above-described configuration, when the chlorine ion concentration or the electrical conductivity is high, the amount of rinse water can be increased to further reduce the chlorine content contained in the medium particles.

同第三の特徴構成は、同請求項3に記載した通り、上述の第一または第二の特徴構成に加えて、前記水切り用の開口は、孔径3mmから5mmの範囲、底面の開孔率15%から25%の範囲に形成されている点にある。In the third feature configuration, as described in claim 3, in addition to the first or second feature configuration described above, the draining opening has a hole diameter in the range of 3 mm to 5 mm, and an opening ratio of the bottom surface. This is in the range of 15% to 25%.

上述の構成によれば、良好な水切り特性が得られる。According to the configuration described above, good drainage characteristics can be obtained.

同第四の特徴構成は、同請求項4に記載した通り、上述の第一から第三の何れかの特徴構成に加えて、前記洗浄槽の内部から槽内上方に向けて洗浄水を供給する注水部を備えている点にある。 In the fourth feature configuration, as described in claim 4, in addition to any of the first to third feature configurations described above, cleaning water is supplied from the inside of the cleaning tank toward the upper side in the tank. It is in the point equipped with the water injection part to do.

洗浄槽に充填された洗浄水の一部が排水部から流出するため、補充する必要がある。そのため、洗浄槽の内部から槽内に洗浄水を供給する注水部を設けることにより、洗浄水を補充することができる。このとき、槽内上方に向けて洗浄水を供給することにより、槽内を沈降する粉粒体に対向する洗浄水の流れが形成され、団子状に固まって沈降する粉粒体が解され、障害物質の含有量が多い粒径の小さな粉粒体が、洗浄水の流れに沿って洗浄されながら上方に浮遊し、排水部から排出されるようになる。 Since a part of the washing water filled in the washing tank flows out from the drainage part, it needs to be replenished. Therefore, the cleaning water can be replenished by providing a water injection unit that supplies the cleaning water from the inside of the cleaning tank into the tank. At this time, by supplying washing water upward in the tank, a flow of washing water is formed opposite to the powder particles that settle in the tank, and the powder particles that settle and settle in a dumpling form are solved. A small granular material having a large particle size and a large amount of an obstructing substance floats upward while being washed along the flow of washing water, and is discharged from the drainage section .

以上説明した通り、本発明によれば、設備を簡素化して洗浄水量を低減しながらも、粉粒体を分級して、水溶性成分や重金属等の障害物質を効率的に除去することができる湿式選別装置を提供することができるようになった。 As described above, according to the present invention, while simplifying the equipment and reducing the amount of washing water, it is possible to classify powder particles and efficiently remove obstacle substances such as water-soluble components and heavy metals. A wet sorting apparatus can be provided.

以下に、本発明による湿式選別装置が粉粒体処理システム1に適用される例を図面に基づいて説明する。ここでは、湿式選別装置により、金属類、ガラ類(石やガラス片等)さらには有機質材(ゴム、プラスチック、紙、繊維、木片等)といった粗大物が混入した粒径200mm以下の焼却灰を洗浄選別する場合を説明する。   Hereinafter, an example in which the wet sorting apparatus according to the present invention is applied to the granular material processing system 1 will be described based on the drawings. Here, incineration ash with a particle size of 200 mm or less mixed with metals, glass (stones, glass pieces, etc.) and organic materials (rubber, plastic, paper, fiber, wood pieces, etc.) A case of cleaning selection will be described.

焼却灰はその粒径により塩素含有量が異なり、粒径が小さいほど塩素含有量が多い。本粉粒体処理システムでは、塩素含有量に基づいて粒径2mm以上の粗粒物(以下、「粗粒灰」とも記す。)と、粒径0.15mm〜2mmの細粒物(以下、「細粒灰」とも記す。)と、0.15mmより小径の微粒物(以下、「微粒灰」とも記す。)に分級し、夫々において洗浄条件を変えることで効率的に脱塩素処理が行なわれる。   Incinerated ash has a different chlorine content depending on its particle size, and the smaller the particle size, the higher the chlorine content. In the present granular material processing system, a coarse particle having a particle diameter of 2 mm or more (hereinafter also referred to as “coarse ash”) and a fine particle having a particle diameter of 0.15 mm to 2 mm (hereinafter, referred to as “coarse ash”) based on the chlorine content. Demineralizing treatment is performed efficiently by classifying into fine particles having a diameter smaller than 0.15 mm (hereinafter also referred to as “fine ash”) and changing the cleaning conditions in each case. It is.

図7に示すように、粉粒体処理システム1は、処理対象物を洗浄しながら粗大物と粉粒体とに選別するとともに粉粒体を微粒物と微粒物より粒径が大きい中粒物(粗粒灰及び細粒灰)に分級する湿式選別装置2と、湿式選別装置2で分級された微粒物を再洗浄する第一の再洗浄手段4と、湿式選別装置2で分級された中粒物を再洗浄する第二の再洗浄手段6を備えている。   As shown in FIG. 7, the granular material processing system 1 selects a coarse material and a granular material while washing the object to be processed, and the granular material has a larger particle size than the fine particles and the fine particles. The wet sorting device 2 for classifying (coarse ash and fine ash), the first re-washing means 4 for re-washing the fine particles classified by the wet sorting device 2, A second recleaning means 6 for recleaning the granules is provided.

さらに、第一の再洗浄手段4から排出された洗浄排水を前記湿式選別装置2へ返送する第一の循環経路8と、第二の再洗浄手段6から排出された洗浄排水を第二の再洗浄手段へ返送する第二の循環経路9を備え、それぞれの循環経路を介して返送された洗浄排水を洗浄水として再利用するように構成されている。   Further, the cleaning wastewater discharged from the first re-cleaning means 4 is returned to the wet sorting device 2 and the cleaning wastewater discharged from the second re-cleaning means 6 is returned to the second re-cleaning means 2. A second circulation path 9 for returning to the cleaning means is provided, and the cleaning waste water returned through each circulation path is reused as cleaning water.

図1から図3に示すように、湿式選別装置2は、洗浄水が充填された側面視U字管形状の洗浄槽20と、洗浄槽20の一方の開口部20aに処理対象物を投入する投入部としての振動式のフィーダ24と、洗浄槽20の他方の開口部20bから洗浄水を脈動させる脈動発生装置30と、フィーダ24で投入された粉粒状の処理対象物に含まれる粗大物を洗浄槽20内で洗浄して、粗大物のうち重量物を分離搬出するコンベア装置22と、洗浄槽20の上層の洗浄水を粗大物のうち軽量物とともに重量物の搬出方向と対向する方向に排水する排水部としての溢流堰26と、洗浄槽20の底部20dに沈降した処理対象物を洗浄槽20の外部に搬出する複数のバケット29aを有するコンベア装置29等を備えている。   As shown in FIG. 1 to FIG. 3, the wet sorting apparatus 2 inputs a processing object into a cleaning tank 20 having a U-shaped side view filled with cleaning water and one opening 20 a of the cleaning tank 20. A vibratory feeder 24 serving as a charging unit, a pulsation generator 30 that pulsates cleaning water from the other opening 20 b of the cleaning tank 20, and a coarse material contained in the granular processing object charged by the feeder 24 The conveyor device 22 that separates and carries out heavy objects out of the coarse material in the washing tank 20 and the cleaning water in the upper layer of the washing tank 20 in the direction opposite to the heavy material carry-out direction together with the lighter ones in the coarse material. An overflow weir 26 serving as a drainage unit for draining, and a conveyor device 29 having a plurality of buckets 29a for carrying out a processing object settled on the bottom 20d of the cleaning tank 20 to the outside of the cleaning tank 20 are provided.

コンベア装置22は、駆動側プーリ22a及び従動側プーリ22bに網目状の孔部を備えた搬送面を備えた無端状のコンベアベルト22cが巻き付けられ、コンベアベルト22cの一部が洗浄槽20の一方の開口部20aの一端側から他端側にかけて浸漬するように配置されている。   In the conveyor device 22, an endless conveyor belt 22 c having a conveyance surface with mesh holes is wound around the driving pulley 22 a and the driven pulley 22 b, and a part of the conveyor belt 22 c is one side of the cleaning tank 20. It arrange | positions so that it may immerse from the one end side of the opening part 20a to the other end side.

洗浄槽20の一方の開口部20aは、正面視で他方の開口部20bよりも横方向に延出形成され、その上部にはコンベアベルト22cの移動方向(図1中、右から左への方向)とは逆方向に向けて水流を形成する給水ノズル23a、23b、23c、23dが配置されている。   One opening 20a of the cleaning tank 20 is formed so as to extend in a lateral direction from the other opening 20b in a front view, and a moving direction of the conveyor belt 22c (a direction from right to left in FIG. 1) Water supply nozzles 23a, 23b, 23c, and 23d that form a water flow in the opposite direction to the above are disposed.

尚、洗浄槽20の形状は、側面視U字管形状に限らず、側面視V字管形状となるように構成してもよい。また、一方の開口部20aと他方の開口部20bの横方向の長さが等しい形状に構成してもよい。さらに、図3に示すように、処理対象物が沈降する底部20dが、側面視U字管形状の洗浄槽20から鉛直壁で下方に延出形成されるものに限らず、図3に破線で示すように、上方ほど幅広となる傾斜壁で下方に延出形成されるものであってもよい。   The shape of the cleaning tank 20 is not limited to the U-shaped tube shape when viewed from the side, and may be configured to have a V-shaped tube shape when viewed from the side. Moreover, you may comprise in the shape where the length of the horizontal direction of one opening part 20a and the other opening part 20b is equal. Furthermore, as shown in FIG. 3, the bottom portion 20 d on which the processing object sinks is not limited to the one in which the bottom wall U-shaped cleaning tank 20 extends downward from the vertical wall, but a broken line in FIG. 3. As shown, it may be formed to extend downward with an inclined wall that becomes wider toward the top.

また、洗浄槽20の形状はU字管形状に構成されるものに限らず、上部が二つに分岐し下部が連結された管形状であれば、V字管形状やY字管形状であってもよい。   Further, the shape of the cleaning tank 20 is not limited to a U-shaped tube shape, and may be a V-shaped tube shape or a Y-shaped tube shape as long as the upper portion is branched into two and the lower portion is connected. May be.

給水ノズル23a、23b、23c、23dからの噴射水により形成される水流の下流側には、上層の洗浄水を排水する溢流堰26が設けられ、その上方には、処理対象物を搬送するベルトコンベア装置36と、ベルトコンベア装置36によって搬送された処理対象物を洗浄槽20に投入する振動式のフィーダ24が配置されている。   An overflow weir 26 is provided on the downstream side of the water flow formed by the water jets from the water supply nozzles 23a, 23b, 23c, and 23d. A belt conveyor device 36 and a vibratory feeder 24 for placing the processing object conveyed by the belt conveyor device 36 into the cleaning tank 20 are arranged.

さらに、洗浄槽20は、コンベアベルト22cの延出方向に沿って、側面視U字状の隔壁20cにより三領域に分割され、一方の開口部20a側に延出した隔壁20cの上縁より上方の水面近傍で処理対象物が分離される分離領域が形成されている。   Further, the cleaning tank 20 is divided into three regions along the extending direction of the conveyor belt 22c by a U-shaped partition wall 20c in a side view, and above the upper edge of the partition wall 20c extending to the one opening 20a side. A separation region is formed in which the object to be treated is separated in the vicinity of the water surface.

脈動発生装置30は、洗浄槽20の他方の開口部20bに設置され、隔壁20cで仕切られた三領域の夫々に対応して配置された、ベローズ37、ロッド32、プランジャ31及びエキセントリックシーブ33と、各エキセントリックシーブ33の回転軸に連結された単一のモータ34で構成されている。   The pulsation generator 30 is installed in the other opening 20b of the cleaning tank 20, and is arranged corresponding to each of the three regions partitioned by the partition wall 20c, and a bellows 37, a rod 32, a plunger 31, and an eccentric sheave 33; , Each of the eccentric sheaves 33 is composed of a single motor 34 connected to the rotating shaft.

モータ34の回転数を制御するインバータ装置が設けられ、モータ34の回転に伴なってエキセントリックシーブ33が回転し、ロッド32を介してプランジャ31が上下動する。プランジャ31の上下動に伴なってベローズ37が伸縮作動することにより、洗浄槽21の一方の開口部20aの水面が上下方向に脈動する。   An inverter device for controlling the rotational speed of the motor 34 is provided. The eccentric sheave 33 rotates as the motor 34 rotates, and the plunger 31 moves up and down via the rod 32. As the bellows 37 expands and contracts as the plunger 31 moves up and down, the water surface of one opening 20a of the cleaning tank 21 pulsates in the up and down direction.

尚、脈動発生装置30に、上下動するプランジャ31のストローク長を調整するストローク長調整機構(図示せず)を備えることにより、脈動する液面の高さを変更することができ、後述の比重分離及び沈降速度による粉流体の分離の精度が調整可能になる。   In addition, by providing the pulsation generator 30 with a stroke length adjustment mechanism (not shown) that adjusts the stroke length of the plunger 31 that moves up and down, the height of the pulsating liquid surface can be changed. The accuracy of the separation of the pulverized fluid by the separation and sedimentation speed can be adjusted.

ストローク長調整機構は、プランジャ31の取付け位置を上下方向に調整する機構、ロッド32の長さを調整する機構、またはロッド32のエキセントリックシーブ33への取付け位置をエキセントリックシーブ33の径方向に調整する機構の何れかまたはそれらを組合せることにより実現できる。   The stroke length adjustment mechanism adjusts the attachment position of the plunger 31 in the vertical direction, the mechanism for adjusting the length of the rod 32, or the attachment position of the rod 32 to the eccentric sheave 33 in the radial direction of the eccentric sheave 33. It can be realized by any of the mechanisms or a combination thereof.

三領域に対応して設けられた三つのエキセントリックシーブ33は、夫々に異なる偏心位置で回転軸35が取付けられ、夫々の領域で位相が異なる脈動が付与される。   The three eccentric sheaves 33 provided corresponding to the three regions are provided with the rotating shafts 35 at different eccentric positions, and are given pulsations having different phases in the respective regions.

フィーダ24から洗浄水槽20に投入された処理対象物は、洗浄水の上下方向の脈動により分離領域で分散され、洗浄されながら比重分離される。   The processing object thrown into the washing water tank 20 from the feeder 24 is dispersed in the separation region by the pulsation in the vertical direction of the washing water and separated by specific gravity while being washed.

灰に混入した粗大物のうち比重の大きな金属類、ガラ類(石やガラス片等)は、付着した灰が洗浄水によって除去されながら分離領域で沈降し、コンベアベルト22cによって粗大物搬出口25から搬出され、比重の小さな有機質材(ゴム、プラスチック、紙、繊維、木片等)は、水面に浮上して給水ノズル23a、23b、23c、23dからの噴射水による水流に従って溢流堰26から搬出される。尚、溢流堰26からの排水は排水樋27を介して水切りスクリーン28に導かれる。   Of the coarse materials mixed in the ash, metals and glass having a large specific gravity (stones, glass pieces, etc.) settle in the separation region while the attached ash is removed by the washing water, and the coarse material unloading port 25 by the conveyor belt 22c. Organic materials (rubber, plastic, paper, fiber, wood chips, etc.) with a small specific gravity float on the water surface and are carried out from the overflow weir 26 according to the water flow from the water supply nozzles 23a, 23b, 23c, 23d. Is done. The drainage from the overflow weir 26 is guided to a draining screen 28 via a drainage basin 27.

即ち、湿式選別装置2では、処理対象物に混入した粗大物が、比重の大きい粗大物と比重の小さい粗大物に選別される選別工程が実行される。   That is, in the wet sorting apparatus 2, a sorting step is performed in which the coarse material mixed in the object to be processed is sorted into a coarse material having a large specific gravity and a coarse material having a small specific gravity.

また、図4に示すように、洗浄槽20に投入された焼却灰は、分離領域で洗浄水の上下方向の脈動により分散され、沈降速度が大きく上方向の脈流に抗して沈降する中粒物(粗粒灰と細粒灰)Aが水槽内に沈降し、沈降速度の小さい微粒灰Bが給水ノズル23a、23b、23c、23dによる水流に従って洗浄水中を浮遊して溢流堰26から排水樋27に流出する。   In addition, as shown in FIG. 4, the incinerated ash charged into the washing tank 20 is dispersed by the pulsation in the vertical direction of the washing water in the separation region, and the sedimentation speed is large and settles against the upward pulsating flow. Granules (coarse ash and fine ash) A settle in the water tank, and fine ash B with a low sedimentation rate floats in the wash water according to the water flow by the water supply nozzles 23a, 23b, 23c, and 23d and flows from the overflow weir 26. It flows into the drainage basin 27.

即ち、湿式選別装置2では、洗浄槽20内での沈降速度差によって微粒物と微粒物より粒径が大きい中粒物とに分離され、微粒物が上層の洗浄水とともに溢流堰26から搬出され、中粒物が洗浄槽20に沈降する分級工程が実行される。   That is, in the wet sorting apparatus 2, the fine particles are separated into medium particles having a particle size larger than the fine particles due to the difference in settling speed in the cleaning tank 20, and the fine particles are carried out from the overflow weir 26 together with the upper cleaning water. Then, a classification process in which the medium particles settle in the washing tank 20 is executed.

このような比重選別工程及び分級工程の過程で、粗大物や粉粒体に付着した塩分等の障害物質が洗浄除去される。   In the course of the specific gravity sorting step and the classification step, obstructive substances such as salt adhering to coarse substances and granular materials are washed away.

図1、図2及び図4に示すように、フィーダ24と溢流堰26との間に、洗浄液を噴射供給する給水ノズル23eが配置され、フィーダ24から投入された焼却灰が沈降速度差により二層に分離するまでの間に、溢流堰26に向けて流れる焼却灰に向けて給水ノズル23eから洗浄水を噴射供給するように構成されている。   As shown in FIGS. 1, 2, and 4, a water supply nozzle 23 e that injects and supplies the cleaning liquid is disposed between the feeder 24 and the overflow weir 26, and the incinerated ash introduced from the feeder 24 is caused by the difference in sedimentation speed. Until the two layers are separated, the cleaning water is jetted and supplied from the water supply nozzle 23e toward the incinerated ash flowing toward the overflow weir 26.

例えば、粒径が大きな灰であっても半乾きの状態で投入されると十分に沈降せずに溢流堰から流出する虞があるが、給水ノズル23eから焼却灰に洗浄液を噴射供給することにより、粒径が大きな中粒物を速やかに沈降させることができる。また、中粒物と微粒物が団子状に固まった焼却灰であっても、給水ノズル23eから噴射供給される洗浄水により速やかに解され、沈降速度による分離が促される。   For example, even if the ash has a large particle size, if it is put in a semi-dry state, there is a risk that the ash will not sink sufficiently and will flow out of the overflow weir. By this, medium particles having a large particle size can be quickly settled. Further, even incinerated ash in which medium and fine particles are solidified in a dumpling form, it is quickly solved by the wash water sprayed and supplied from the water supply nozzle 23e, and the separation by the sedimentation speed is promoted.

従って、フィーダ24と溢流堰26との距離をより短く設定することができ、装置をより小型化することができるようになる。   Accordingly, the distance between the feeder 24 and the overflow weir 26 can be set shorter, and the apparatus can be further downsized.

排水樋27に流出した溢流水は、水切りスクリーン28によって有機質材が除去された後に微粒灰とともに第一の再洗浄装置4(図7参照)に送られる。この時、水切りスクリーン28部では、洗浄水を噴霧して有機質材を洗浄してもよい。   The overflow water flowing out to the drainage basin 27 is sent to the first re-cleaning device 4 (see FIG. 7) together with the fine ash after the organic material is removed by the draining screen 28. At this time, the organic material may be washed by spraying washing water on the draining screen 28 part.

図3及び図6に示すように、洗浄槽20の底部20dに沈降した中粒物は、底部に複数の小径の開口29bが形成された複数のバケット29aが無限軌道に沿って並設されたバケットコンベア機構29によって水切りされながら槽外に搬出され、第二の再洗浄手段6(図7参照)によってさらに洗浄処理される。   As shown in FIG. 3 and FIG. 6, the medium particles settled on the bottom portion 20 d of the cleaning tank 20 have a plurality of buckets 29 a in which a plurality of small-diameter openings 29 b are formed at the bottom portion arranged side by side along an endless track. While being drained by the bucket conveyor mechanism 29, it is carried out of the tank and further cleaned by the second re-cleaning means 6 (see FIG. 7).

搬送中にバケット29aで掻き揚げられた中粒物と洗浄水のうち、主に洗浄水が開口29bから流出することにより、洗浄水由来の塩素の含有量を低減させた中粒物を次工程に供給することができる。   Of the medium particles and washing water that have been lifted up by the bucket 29a during transport, mainly the washing water flows out from the opening 29b, thereby reducing the content of chlorine derived from the washing water to the next step. Can be supplied to.

孔径3mmから5mmの範囲で、底面の開孔率15%から25%の範囲で開口29bを形成すると、搬出される中粒物の含水率が50%程度となり、良好な水切り特性が得られる。   When the opening 29b is formed in the range of the hole diameter of 3 mm to 5 mm and the opening ratio of the bottom surface of 15% to 25%, the moisture content of the medium particles to be carried out is about 50%, and good drainage characteristics are obtained.

例えば、開口29bが3mmの角孔で底面の開孔率25%となるように形成された織網でバケット29aの底部を構成すると、中粒物の含水率が52%となり、開口29bがφ3mmの丸孔で底面の開孔率17%となるように形成された打ち抜き板でバケット29aの底部を構成すると、中粒物の含水率が約50%と良好な水切り特性が得られる。尚、開口29bが1mmの角孔で底面の開孔率22%となるように形成された織網でバケット29aの底部を構成すると、バケット29aの中粒物に水溜りが形成され、水抜きができない。   For example, when the bottom portion of the bucket 29a is formed of a woven mesh formed so that the opening 29b is a 3 mm square hole and the bottom surface has an opening rate of 25%, the moisture content of the medium grain is 52%, and the opening 29b has a diameter of 3 mm. When the bottom portion of the bucket 29a is formed of a punched plate formed so as to have an opening rate of 17% on the bottom surface of the round hole, a good water draining characteristic with a moisture content of about 50% can be obtained. If the bottom portion of the bucket 29a is formed of a woven mesh formed so that the opening 29b is a 1 mm square hole and the opening ratio of the bottom surface is 22%, a puddle is formed in the medium particles of the bucket 29a, and water is drained. I can't.

さらに、図6(b)に示すように、バケット式のコンベア装置29には、水切り後の中粒物にリンス水を噴射供給する給水ノズル29cを備え、中粒物の間隙に残存する塩素の濃度が高い洗浄水をリンス水で置換するように構成されている。尚、リンス水は、第二循環経路9を経由した洗浄排水が好適に用いられるが、新規水が用いられるものであってもよい。   Further, as shown in FIG. 6 (b), the bucket type conveyor device 29 is provided with a water supply nozzle 29c for injecting rinsing water to spray the medium particles after draining, so that the chlorine remaining in the intermediate particles can be removed. The washing water having a high concentration is replaced with rinsing water. In addition, although the rinse water which passed through the 2nd circulation path 9 is used suitably for rinse water, a new water may be used.

つまり、洗浄槽20の底部20dに沈降した粒径の大きな中粒物がバケット29aによって掻き揚げられ槽外に搬出される過程で、障害物質の濃度が高い洗浄水が開孔から排水され、更に、水切り後の処理対象物に給水ノズル29cからリンス水を噴射供給することにより、粉粒体に含まれる障害物質の濃度を大きく低減させることができる。   That is, in the process in which the medium-sized matter having a large particle size that has settled at the bottom 20d of the cleaning tank 20 is lifted up by the bucket 29a and carried out of the tank, the cleaning water having a high concentration of the obstacle substance is drained from the opening. By spraying rinse water from the water supply nozzle 29c onto the processing target after draining, the concentration of the obstacle substance contained in the powder can be greatly reduced.

洗浄槽20に充填された洗浄水の塩素イオン濃度または電気伝導度を計測するセンサを洗浄槽20内に配置して、当該センサの検出値に基づいて、給水ノズル29cから噴射供給するリンス水の水量を調整することが好ましい。塩素イオン濃度または電気伝導度が高いときには、リンス水の水量を増加して中粒物に含まれる塩素含有量の更なる低減を図ることができる。   A sensor for measuring the chlorine ion concentration or electrical conductivity of the cleaning water filled in the cleaning tank 20 is disposed in the cleaning tank 20, and rinse water supplied and supplied from the water supply nozzle 29c based on the detection value of the sensor. It is preferable to adjust the amount of water. When the chlorine ion concentration or electrical conductivity is high, the amount of rinsing water can be increased to further reduce the chlorine content contained in the medium grain.

溢流堰26から流出する洗浄水は、第一の循環経路9(図7参照)を介して貯留槽100に貯水され、その後、上述の給水ノズル23a、23b、23c、23d、23e、及び、洗浄槽20の底部近傍に配置された給水ノズル20eを介して洗浄槽20に循環される。   Wash water flowing out of the overflow weir 26 is stored in the storage tank 100 via the first circulation path 9 (see FIG. 7), and then the above-described water supply nozzles 23a, 23b, 23c, 23d, 23e, and The water is circulated to the cleaning tank 20 through a water supply nozzle 20e disposed in the vicinity of the bottom of the cleaning tank 20.

給水ノズル20eからの洗浄水の噴射方向は、処理対象物が投入される一方の開口部20aに向けられている。流量調整可能なポンプを介して給水ノズル20eにより上方に噴射供給された洗浄水は、槽内を沈降する粉粒体に対向する洗浄水の流れを形成し、団子状に固まって沈降する粉粒体が解され、障害物質の含有量が多い粒径の小さな粉粒体が、洗浄水の流れに沿って洗浄されながら上方に浮遊し、溢流堰26から排出される。即ち、ポンプと給水ノズル20eにより洗浄槽20の内部から槽内上方に向けて洗浄水を供給する注水部が構成されている。   The direction in which the washing water is ejected from the water supply nozzle 20e is directed to the one opening 20a into which the object to be treated is introduced. The washing water sprayed and supplied upward by the water supply nozzle 20e through the pump capable of adjusting the flow rate forms a flow of washing water that opposes the powder particles that settle in the tank, and the powder particles that solidify and settle in a dumpling form. The body is unraveled, and the small granular material with a large content of the obstacle substance floats upward while being washed along the flow of the washing water, and is discharged from the overflow weir 26. That is, the water injection part which supplies cleaning water from the inside of the washing tank 20 toward the inside of the tank is constituted by the pump and the water supply nozzle 20e.

尚、第一の循環経路8から供給される再洗浄水を給水ノズル23a、23b、23c、23d、23eを介して供給するルートと、給水ノズル20eを介して供給するルートの夫々のルートを介した再洗浄水の供給比率を調整することが好ましい。給水ノズル20eから供給する比率を調整し、洗浄槽20の上昇流の速度を調整することによって、粉粒体の沈降速度を制御して分級する粒径を設定することも可能となる。   The re-washing water supplied from the first circulation path 8 is routed through each of a route for supplying water via the water supply nozzles 23a, 23b, 23c, 23d, and 23e and a route for supplying the rewash water via the water supply nozzle 20e. It is preferable to adjust the supply ratio of the rewashed water. By adjusting the ratio supplied from the water supply nozzle 20e and adjusting the speed of the upward flow in the cleaning tank 20, it is possible to set the particle size to be classified by controlling the sedimentation speed of the powder.

コンベア装置22のコンベアベルト22cは、目幅が5から15mmの織網で構成され、洗浄槽20内で、粗大物として沈降するボルト類、金属片、ガラス片等の不適物を受け止めるとともに、網目から中粒物を底部に向けて沈降するように通過させる。   The conveyor belt 22c of the conveyor device 22 is composed of a woven mesh having a mesh width of 5 to 15 mm, receives unsuitable materials such as bolts, metal pieces, glass pieces, etc. that settle as coarse objects in the washing tank 20, and has a mesh. The medium particles are allowed to pass through to settle toward the bottom.

例えば、目幅が10mmの角孔を開口率70%となるように、線径2mmの鋼線で構成した織網を好適に用いることができる。目幅が5mmより小さくなると網目の閉塞により、粗大物と中粒物を分離できなくなり、15mmを超えると粗大物が網目を通り抜けることが多く、中粒物に対するその後の洗浄処理に不都合を来たす。   For example, a woven net made of a steel wire having a wire diameter of 2 mm can be suitably used so that a square hole having a mesh width of 10 mm has an opening ratio of 70%. When the mesh width is smaller than 5 mm, coarse particles and medium particles cannot be separated due to clogging of the mesh, and when the mesh width exceeds 15 mm, coarse particles often pass through the mesh, resulting in inconvenience in the subsequent washing treatment for the medium particles.

また、打ち抜き網では、強度を確保するために開口率が制限され、中粒物が網上に残存するため、排出された金属類に灰が再付着して、資源化が妨げられるという不都合がある。   Moreover, in the punched net, the opening ratio is limited in order to ensure strength, and the medium grain remains on the net, so that the ash reattaches to the discharged metals, which hinders resource recycling. is there.

図1、図3及び図5に示すように、洗浄槽20内で粗大物を受け止め、粗大物搬出口25で粗大物が離脱されたコンベアベルト22cは、洗浄槽20の外部に設けられた清掃機構21により清掃され、網目に詰った金属類等が除去される。   As shown in FIGS. 1, 3, and 5, the conveyor belt 22 c that receives a coarse object in the cleaning tank 20 and from which the coarse object is detached at the coarse object outlet 25 is a cleaning provided outside the cleaning tank 20. Metals and the like that are cleaned by the mechanism 21 and clogged are removed.

清掃機構21は、多数の細い鋼線が支持部に固定されたブラシで構成され、コンベアベルト22cの移動に伴なってコンベアベルト22cの裏面とブラシが摺動することにより、網目に詰った金属類等が落下除去される。   The cleaning mechanism 21 is composed of a brush in which a large number of thin steel wires are fixed to a support portion, and the back surface of the conveyor belt 22c and the brush slide with the movement of the conveyor belt 22c. Kinds are dropped and removed.

コンベアベルト22cの下方にはホッパまたはシュート11が設けられ、コンベアベルト22cから自由落下した粗大物や、清掃機構21により除去された粗大物が当該ホッパまたはシュート11に落下し、その下部に配置された粗大物搬送用のコンベア装置12により、粗大物搬出口25で離脱した粗大物とともに、図7に示す金属回収部10に搬送されて、金属回収部10に備えた磁選機により金属とガラ類に分離して回収される。   A hopper or chute 11 is provided below the conveyor belt 22c, and a coarse object that has dropped freely from the conveyor belt 22c or a coarse object that has been removed by the cleaning mechanism 21 falls on the hopper or chute 11 and is disposed below it. 7 is transported to the metal recovery unit 10 shown in FIG. 7 together with the coarse material separated at the bulky material outlet 25 by the conveyor device 12 for transporting the coarse material, and metal and glass are collected by the magnetic separator provided in the metal recovery unit 10. It is separated and collected.

また、図8に示すように、粗大物搬出口25の上方であって、駆動側プーリ22aの下流側に清掃機構21を設けることにより、網目に詰った金属類等を粗大物搬出口25から落下させるように構成してもよい。   Further, as shown in FIG. 8, by providing a cleaning mechanism 21 above the coarse object outlet 25 and on the downstream side of the driving pulley 22a, the metal or the like clogged in the mesh is removed from the coarse object outlet 25. You may comprise so that it may fall.

図7に示すように、水切りスクリーン28を経た溢流水に含まれる微粒物を洗浄する第一の再洗浄手段4が設けられている。以下、詳述する。   As shown in FIG. 7, the first re-cleaning means 4 for cleaning the fine particles contained in the overflow water that has passed through the draining screen 28 is provided. Details will be described below.

水切りスクリーン28を経た溢流水が必要に応じて設けた中継槽40に蓄積され、攪拌ポンプにより濃度を均一に攪拌され、溢流水に含まれる微粒灰がポンプにより濃縮装置42としてのシックナーに送られて濃縮される。尚、濃縮装置42として、湿式サイクロン、ベルト濃縮機、遠心濃縮機等の公知の装置を用いることもできる。また、中継槽40には硫酸バンド等の凝集剤、pH調整剤、キレート剤等の薬品41を添加してもよい。   The overflow water passing through the draining screen 28 is accumulated in the relay tank 40 provided as necessary, the concentration is uniformly stirred by the stirring pump, and the fine ash contained in the overflow water is sent to the thickener as the concentrator 42 by the pump. And concentrated. As the concentrating device 42, a known device such as a wet cyclone, a belt concentrator, or a centrifugal concentrator can be used. In addition, a chemical agent 41 such as a flocculant such as a sulfuric acid band, a pH adjuster, or a chelating agent may be added to the relay tank 40.

前記濃縮された微粒灰は、シックナーの底部から引き抜かれ、中継槽43に送られて給水槽101から供給される新たな洗浄水で攪拌洗浄され、その後、脱水洗浄装置44で脱水洗浄されセメント原料に供される。尚、中継槽43を設けることなく、シックナーで濃縮された微粒灰を直接脱水洗浄装置44へ送り、洗浄水を注入しながら脱水してもよい。このような脱水洗浄装置44として、フィルタプレス、遠心分離脱水機、ベルト式脱水機等を用いることができる。洗浄水の供給量は、シックナーの上澄み液の塩分濃度に応じて調整され、塩分濃度が高ければ洗浄水の供給量が増加される。   The concentrated fine ash is pulled out from the bottom of the thickener, sent to the relay tank 43, stirred and washed with new washing water supplied from the water supply tank 101, and then dehydrated and washed by the dehydration washing apparatus 44. To be served. In addition, without providing the relay tank 43, the fine ash concentrated by the thickener may be sent directly to the dehydrating and cleaning device 44 and dehydrated while injecting cleaning water. As such a dehydration washing apparatus 44, a filter press, a centrifugal dehydrator, a belt type dehydrator, or the like can be used. The supply amount of the wash water is adjusted according to the salt concentration of the supernatant of the thickener. If the salt concentration is high, the supply amount of the wash water is increased.

尚、濃縮装置42を設けず、微粒灰を中継槽40から直接脱水洗浄装置44へ送ってもよい。   Note that the fine ash may be sent directly from the relay tank 40 to the dehydrating and cleaning device 44 without providing the concentrating device 42.

脱水洗浄装置44からの洗浄排水は中継槽45に排水され、最終的に貯留槽46に貯水される。   The washing waste water from the dehydrating and cleaning device 44 is drained into the relay tank 45 and finally stored in the storage tank 46.

貯留槽46には高さが異なる二枚の堰で三室に区分され、高い方の堰を溢れた排水が最終の貯留槽47に貯水され、水処理装置で浄化処理された後に系外に排水される。   The storage tank 46 is divided into three chambers by two weirs with different heights, and the waste water overflowing the higher weir is stored in the final storage tank 47 and purified by a water treatment device and discharged outside the system. Is done.

濃縮装置42及び脱水洗浄装置44によって分離され貯留槽46に貯水された洗浄排水は,ポンプによって第一の循環経路8を介して貯留槽100に返送され、貯留槽100から給水ノズル23a、23b、23c、23d、23e、20eを介して洗浄槽20に再供給されて再洗浄水として利用される。   The cleaning wastewater separated by the concentrating device 42 and the dehydrating and cleaning device 44 and stored in the storage tank 46 is returned to the storage tank 100 via the first circulation path 8 by a pump, and the water supply nozzles 23a, 23b, It is re-supplied to the washing tank 20 through 23c, 23d, 23e, and 20e and used as re-washing water.

また、濃縮装置42によって分離された洗浄排水は、障害物質の濃度が高いので、優先的に系外へ排出するため、貯留槽46を介さず貯留槽47へ送り、洗浄水が不足した場合のみ貯留槽46へ送り再洗浄水として利用する構成であってもよい。   In addition, since the cleaning wastewater separated by the concentrating device 42 has a high concentration of obstacle substances, it is preferentially discharged out of the system. Therefore, it is sent to the storage tank 47 without passing through the storage tank 46, and only when the cleaning water is insufficient. It may be configured to be sent to the storage tank 46 and used as rewash water.

微粒灰の塩分含有量は、中粒灰の塩分含有量よりも多く、第一の再洗浄手段4からの洗浄排水の塩分含有量は第二の再洗浄手段6の洗浄排水よりも高いため、第二の再洗浄手段6とは分離して湿式選別手段2へ返送するのである。   The salt content of the fine ash is higher than the salt content of the medium ash, and the salt content of the cleaning effluent from the first recleaning means 4 is higher than the cleaning effluent of the second recleaning means 6, It is separated from the second recleaning means 6 and returned to the wet sorting means 2.

このようにして、湿式選別装置2及び第一の再洗浄手段4では、塩分濃度が高い洗浄排水で洗浄処理されるが、濃縮装置42を経ることにより脱水洗浄装置44に供給される新たな洗浄水(リンス水)の量は極めて僅かに抑えることができる。   In this way, in the wet sorting device 2 and the first re-cleaning means 4, the cleaning treatment is performed with the cleaning wastewater having a high salt concentration, but a new cleaning is supplied to the dehydration cleaning device 44 through the concentration device 42. The amount of water (rinse water) can be suppressed very slightly.

第二の再洗浄手段6は、バケットコンベア機構29によって槽外に搬出された中粒物を粗粒灰と細粒灰に分級する分級装置61と、分級装置61で分級された細粒物を再洗浄する洗浄装置62を備えている。分級装置61は湿式の振動篩装置で構成され、バケットコンベア機構29からシュート60を介して落下供給される。尚、分級装置61として、スクリーン装置を用いることができる。   The second re-cleaning means 6 classifies the intermediate particles carried out of the tank by the bucket conveyor mechanism 29 into coarse ash and fine ash, and the fine particles classified by the classification device 61. A cleaning device 62 for re-cleaning is provided. The classification device 61 is configured by a wet vibration sieve device, and is supplied by dropping from the bucket conveyor mechanism 29 via the chute 60. Note that a screen device can be used as the classification device 61.

シュート60及び分級装置61には、第二の循環経路9を介して循環供給された塩分濃度が低い洗浄排水が噴霧供給されるとともに、分級装置61の下流側では給水槽101から新たな洗浄水が噴霧供給され、分級された粗粒灰はそのまま水切りしてセメント原料として供される。粒径が大きな粗粒灰には付着塩類が僅かであるため、それほど洗浄する必要が無いのである。   The chute 60 and the classification device 61 are spray-fed with cleaning wastewater having a low salinity concentration circulated through the second circulation path 9, and new washing water is supplied from the water supply tank 101 on the downstream side of the classification device 61. Is spray-fed and the classified coarse ash is drained as it is and used as a cement raw material. Coarse ash having a large particle size has a small amount of adhering salts, and therefore does not require much washing.

洗浄装置62は、分級装置61を経た細粒物及び洗浄排水を貯留する中継槽63と、中継槽63で再度攪拌洗浄された細粒灰を固液分離する固液分離機64としての湿式サイクロンと、湿式サイクロンで固液分離された細粒灰を洗浄する洗浄槽65を備えている。   The cleaning device 62 includes a relay tank 63 that stores fine particles and cleaning wastewater that have passed through the classification device 61, and a wet cyclone as a solid-liquid separator 64 that solid-liquid separates the fine ash that has been stirred and washed again in the relay tank 63. And the washing tank 65 which wash | cleans the fine ash solid-liquid-separated with the wet cyclone is provided.

灰沈降槽で沈降した細粒灰は、灰掻揚げコンベア66で搬出されながら給水槽101から供給される新たな洗浄水(リンス水)で濯がれて水切りされた後にセメント材料として供される。尚、洗浄槽65の溢流水は中継槽63に循環供給される。   Fine ash settled in the ash settling tank is rinsed with new washing water (rinse water) supplied from the water supply tank 101 while being carried out by the ash lifting conveyor 66, and then used as a cement material. . The overflow water in the cleaning tank 65 is circulated and supplied to the relay tank 63.

湿式サイクロンで分離された洗浄排水は、洗浄水として上述したシュート60及び分級装置61に循環供給され、余剰の洗浄排水が貯留槽100に貯水された後に、湿式選別装置2の洗浄水として供給される。湿式サイクロンで分離された洗浄排水には湿式選別装置2で十分に分離されなかった微粒灰が含まれており、このような微粒灰は第二循環経路9を経て、再度、湿式選別装置2で分級される。尚、固液分離機64は湿式サイクロンに限られるものではなく、公知の脱水機、沈殿槽等により細粒灰と洗浄排水を分離する構成であってもよい。   The washing wastewater separated by the wet cyclone is circulated and supplied as washing water to the chute 60 and the classification device 61 described above, and after the excess washing wastewater is stored in the storage tank 100, it is supplied as washing water for the wet sorting device 2. The The washing waste water separated by the wet cyclone contains fine ash that has not been sufficiently separated by the wet sorting device 2, and such fine ash passes through the second circulation path 9 and again in the wet sorting device 2. Classified. The solid-liquid separator 64 is not limited to a wet cyclone, and may be configured to separate fine ash and washing wastewater by a known dehydrator, a sedimentation tank, or the like.

第二の循環経路9は、洗浄槽65からの洗浄排水を中継槽63へ返送する循環経路91と、固液分離機64の排水を分級装置61へ返送する循環経路92を備えている。   The second circulation path 9 includes a circulation path 91 for returning the cleaning wastewater from the cleaning tank 65 to the relay tank 63 and a circulation path 92 for returning the wastewater of the solid-liquid separator 64 to the classification device 61.

つまり、本発明による粉粒体処理システムは、微粒物を再洗浄する第一の再洗浄手段と、中粒物を再洗浄する第二の再洗浄手段と、第一の再洗浄手段から排出された洗浄排水を湿式選別装置へ返送する第一の循環経路と、第二の再洗浄手段から排出された洗浄排水を第二の再洗浄手段へ返送する第二の循環経路を備え、それぞれの循環経路を介して返送された洗浄排水を洗浄水として再利用するように構成されている。   That is, the granular material processing system according to the present invention is discharged from the first re-cleaning means for re-cleaning the fine particles, the second re-cleaning means for re-cleaning the medium particles, and the first re-cleaning means. Provided with a first circulation path for returning the washed wastewater to the wet sorting device and a second circulation path for returning the washed wastewater discharged from the second rewashing means to the second rewashing means. The washing waste water returned through the route is reused as washing water.

従って、設備を簡素化して洗浄水量を低減しながらも、処理対象物に混在する粗大物を洗浄分離除去し、洗浄排水の循環経路を二系統に分離することで、粉粒体から水溶性成分や重金属等の障害物質を効率的に除去することができるようになる。   Therefore, while simplifying the equipment and reducing the amount of water to be washed, coarse substances mixed in the treatment object are washed and removed, and the circulation path of the washing wastewater is separated into two systems, so that water-soluble components are separated from the granular material. And obstructive substances such as heavy metals can be efficiently removed.

本発明による湿式選別装置は、不法投棄された埋立土壌等、重金属類等により汚染された土壌であって、上述したような粗大物が混入した土壌の粉粒体を資源化して再利用する場合にも適用が可能である。この場合、本発明により土砂から重金属類の汚染物質が洗浄除去される。   The wet sorting device according to the present invention is soil contaminated with heavy metals, such as illegally dumped landfill soil, etc., and when the soil granular material mixed with coarse materials as described above is recycled as resources It can also be applied to. In this case, according to the present invention, heavy metal contaminants are washed and removed from the earth and sand.

以上説明した湿式選別装置の具体的構成は実施形態の記載に限定されるものではなく、本発明による作用効果を奏する範囲において適宜変更設計可能であることはいうまでもない。   It is needless to say that the specific configuration of the wet sorting apparatus described above is not limited to the description of the embodiment, and can be appropriately changed and designed within the scope of the effects of the present invention.

本発明による湿式選別装置を正面から眺めた説明図The explanatory view which looked at the wet sorter by the present invention from the front 同湿式選別装置の平面図Top view of the wet sorting device 同湿式選別装置を側面から眺めた要部説明図Explanatory drawing of the main part of the wet sorting device viewed from the side 同湿式選別装置の洗浄槽の要部説明図Explanatory drawing of the main part of the washing tank of the wet sorting device 同湿式選別装置の搬送装置の要部説明図Explanatory drawing of the main part of the transfer device of the wet sorting device バケット式コンベア装置の要部説明図Explanatory drawing of the main part of the bucket conveyor 粉粒体処理システムのブロック説明図Block explanatory diagram of powder processing system 別実施形態を示し、同湿式選別装置の搬送装置の要部説明図Explanatory drawing of the principal part of the conveying apparatus of the wet sorting apparatus showing another embodiment

1:粉粒体処理システム
2:湿式選別装置
4:第一の再洗浄手段
6:第二の再洗浄手段
8:第一の循環経路
9:第二の循環経路
20:洗浄槽
22:コンベア装置
22a:コンベアベルト
23a、23b、23c、23d、23e、29c:給水ノズル
24:フィーダ
26:溢流堰
29:バケット式のコンベア装置
30:脈動発生装置
40:中継槽
42:濃縮装置(シックナー)
43:中継槽
44:脱水洗浄装置
46,47:貯留槽
61:分級装置
62:洗浄装置
63:中継槽
64:固液分離機(湿式サイクロン)
65:洗浄槽
1: Powder processing system 2: Wet sorting device 4: First re-cleaning means 6: Second re-cleaning means 8: First circulation path 9: Second circulation path 20: Cleaning tank 22: Conveyor device 22a: Conveyor belts 23a, 23b, 23c, 23d, 23e, 29c: Water supply nozzle 24: Feeder 26: Overflow weir 29: Bucket type conveyor device 30: Pulsation generator 40: Relay tank 42: Concentrator (thickener)
43: Relay tank 44: Dehydration cleaning device 46, 47: Storage tank 61: Classification device 62: Cleaning device 63: Relay tank 64: Solid-liquid separator (wet cyclone)
65: Cleaning tank

Claims (4)

洗浄槽に投入された処理対象物を洗浄水で洗浄しながら沈降速度差によって微粒物と微粒物より粒径が大きい中粒物とに分離し、分離された微粒物を上層の洗浄水とともに排水部から排出し、前記洗浄槽に沈降した中粒物をバケット式のコンベア装置により槽外に搬出するように構成された湿式選別装置であって、While washing the treatment object thrown into the washing tank with washing water, it separates into fine particles and medium particles having a larger particle size than the fine particles due to the difference in sedimentation speed, and the separated fine particles are drained together with the upper washing water A wet sorting device configured to discharge the medium particles discharged from the section and settled in the washing tank to the outside of the tank by a bucket type conveyor device,
前記バケット式のコンベア装置のバケットの底部に水切り用の開口が形成され、水切り後の処理対象物にリンス水を噴射供給する給水ノズルを備えている湿式選別装置。A wet-type sorting device having a water supply nozzle that is formed with an opening for draining water at the bottom of the bucket of the bucket-type conveyor device and sprays and feeds rinse water to the processing target after draining.
前記洗浄槽内の洗浄水の塩素イオン濃度または電気伝導度に基づいて、前記給水ノズルから供給されるリンス水の水量が調整される請求項1記載の湿式選別装置。The wet sorting apparatus according to claim 1, wherein an amount of rinse water supplied from the water supply nozzle is adjusted based on a chlorine ion concentration or electrical conductivity of the cleaning water in the cleaning tank. 前記水切り用の開口は、孔径3mmから5mmの範囲、底面の開孔率15%から25%の範囲に形成されている請求項1または2記載の湿式選別装置。3. The wet sorting apparatus according to claim 1, wherein the draining opening is formed in a range of a hole diameter of 3 mm to 5 mm and a bottom surface area of 15% to 25%. 前記洗浄槽の内部から槽内上方に向けて洗浄水を供給する注水部を備えている請求項1から3の何れかに記載の湿式選別装置。The wet sorting apparatus according to any one of claims 1 to 3, further comprising a water injection unit configured to supply cleaning water from the inside of the cleaning tank toward the upper part of the tank.
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CN109604042A (en) * 2018-12-29 2019-04-12 天地(唐山)矿业科技有限公司 A kind of energy saving shallow slot heavy-media separator of width grade pulsation
CN109604042B (en) * 2018-12-29 2021-03-09 天地(唐山)矿业科技有限公司 Wide-size-fraction pulsating shallow-groove heavy-medium separator
CN109821880A (en) * 2019-02-13 2019-05-31 云南天朗环境科技有限公司 A kind of soil high-pressure rotary-spray renovation technique and device
CN109821880B (en) * 2019-02-13 2022-03-29 云南天朗环境科技有限公司 High-pressure rotary spraying repair process and device for soil
KR102364327B1 (en) * 2021-11-09 2022-02-17 주식회사 초당산업 A hybrid type separation discharge device consisting of a one-shot loop type discharge of aggregate and sludge and a two-stage separation of foreign substances

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