JP2008264768A - Treatment method of incineration ash and treatment equipment of incineration ash - Google Patents

Treatment method of incineration ash and treatment equipment of incineration ash Download PDF

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JP2008264768A
JP2008264768A JP2008054173A JP2008054173A JP2008264768A JP 2008264768 A JP2008264768 A JP 2008264768A JP 2008054173 A JP2008054173 A JP 2008054173A JP 2008054173 A JP2008054173 A JP 2008054173A JP 2008264768 A JP2008264768 A JP 2008264768A
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ash
cleaning
incineration
incinerated
washing
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JP5481034B2 (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

<P>PROBLEM TO BE SOLVED: To provide a treatment method of incineration ash capable of reducing a treatment cost for reuse as a cement raw material or the like and efficiently removing chlorine contained in the incineration ash such as main ash and fly ash discharged from an incinerator, and treatment equipment of incineration ash. <P>SOLUTION: The treatment method of the incineration ash for cleaning the incineration ash comprises: a first process of cleaning incineration main ash separated and recovered from the incineration ash while separating unburned matters and inappropriate matters; and a second process of classifying the incineration main ash separated and cleaned in the first process. The incineration main ash separated and recovered from the incineration ash is fed to the first process without being cleaned beforehand. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、粗大物が混入した粉粒状の処理対象物を処理する処理設備に関し、特に、焼却灰を洗浄処理する焼却灰の処理方法及び焼却灰の処理設備に関する。   The present invention relates to a processing facility for processing a granular processing object mixed with a coarse material, and more particularly, to a processing method for incineration ash for cleaning incineration ash and a processing facility for incineration ash.

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、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。   For example, when purifying and reusing contaminated soil where 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.

焼却主灰や飛灰などの焼却灰は、一般に最終処分場に埋立処理され、或いは、溶融炉において高温で溶融処理して化学的に安定したスラグに減容化して処分されているが、近年、最終処分場の容量の飽和などの問題からセメント原料として再利用することが考えられている。   Incineration ash, such as incineration main ash and fly ash, is generally landfilled at the final disposal site, or disposed of in a melting furnace at a high temperature and then reduced to chemically stable slag. In view of problems such as saturation of the capacity of the final disposal site, it is considered to be reused as a raw material for cement.

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、先ず、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必要がある。   In general, when incineration residues such as incineration ash generated in municipal waste incineration facilities are reused as raw materials for cement, it is first necessary to separate and remove coarse materials such as metals, glass, and organic materials from the incineration residues. .

さらに、焼却灰を予熱装置にて予熱処理した後にロータリーキルンなどで焼成する際に、焼却灰に含まれる塩素成分により装置が腐食するという問題があるため、予め焼却灰を水洗処理して塩素を除去する必要がある。   Furthermore, when the incineration ash is preheated with a preheating device and then baked in a rotary kiln, etc., there is a problem that the device is corroded by the chlorine component contained in the incineration ash, so the incineration ash is washed with water in advance to remove chlorine. There is a need to.

また、国内のセメントの消費量の約70%を占める普通ポルトランドセメントの原料として焼却灰を利用する場合は、コンクリート中の鉄筋の腐食を防止するために塩素除去が必要となる。   In addition, when incinerated ash is used as a raw material for ordinary Portland cement, which accounts for about 70% of domestic cement consumption, it is necessary to remove chlorine in order to prevent corrosion of reinforcing bars in concrete.

特許文献1には、都市ゴミ焼却炉より排出される焼却灰を、主灰と飛灰とに別々の受槽に回収する回収工程、該回収工程の主灰受槽の主灰を粉砕し、平均粒径200μm以下の大きさの粉砕粒子を得る粉砕工程、該回収工程の飛灰受槽の飛灰を還元雰囲気下、300ないし450℃の温度で処理してダイオキシン類を分解する脱ダイオキシン工程、及び、粉砕工程より得られる主灰と脱ダイオキシン工程より得られる飛灰とを水洗し、塩素成分が低減された固形分を回収する洗浄工程を含む焼却灰の処理方法が提案されている。
特開2003−103232号公報
Patent Document 1 discloses a recovery process for recovering incineration ash discharged from a municipal waste incinerator into separate receiving tanks for main ash and fly ash, pulverizing the main ash in the main ash receiving tank of the recovery process, A pulverization step for obtaining pulverized particles having a diameter of 200 μm or less, a dedioxin step for decomposing dioxins by treating fly ash in the fly ash receiving tank of the recovery step at a temperature of 300 to 450 ° C. in a reducing atmosphere, and There has been proposed a method for treating incinerated ash that includes a washing step in which the main ash obtained from the pulverization step and the fly ash obtained from the dedioxin step are washed with water and the solid content with reduced chlorine components is recovered.
JP 2003-103232 A

しかし、特許文献1に記載される方法では、粉砕工程より得られる主灰と脱ダイオキシン工程より得られる飛灰とを混合して同時に水洗処理するために、効率が悪いという問題があった。   However, the method described in Patent Document 1 has a problem that the efficiency is poor because the main ash obtained from the pulverization step and the fly ash obtained from the dedioxin step are mixed and simultaneously washed with water.

一般に焼却主灰中の塩素濃度は1%程度であるのに対して、飛灰中の塩素濃度は8〜十数%と非常に高く、これらを纏めて洗浄するのは非効率的であり、多量の洗浄水が必要とされるばかりか、有機分を含まない飛灰と有機分を含む主灰を纏めることにより、大量の洗浄排水を浄化処理するために規模の大きな生物処理槽が必要となるのである。   In general, the chlorine concentration in the incinerated main ash is about 1%, whereas the chlorine concentration in the fly ash is as high as 8 to over 10%, and it is inefficient to wash these together. Not only is a large amount of washing water required, but a large-scale biological treatment tank is required to purify a large amount of washing wastewater by collecting fly ash that does not contain organic components and main ash that contains organic components. It becomes.

また、大半の洗浄装置が焼却主灰中に含まれる残飯、紙、木片、繊維類、ビニールなどの未燃物、ガラ類、金属類などの雑多な固形物を想定したものではないため、これらを効率的に除去しなければならないという課題もあった。   In addition, most cleaning equipment is not intended for miscellaneous solids such as leftovers, paper, wood chips, fibers, vinyl, and other unburned materials contained in incinerator main ash, glass, and metals. There was also a problem that it must be removed efficiently.

このように、粗大物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効率的に除去する必要性は、焼却灰に限らず、雑多な廃棄物が不法投棄された汚染土壌等の粉粒体に共通している。   In this way, the necessity of efficiently removing obstacle substances mixed in the processing object by washing the granular processing object mixed with a coarse material is not limited to incineration ash, and miscellaneous waste is illegal. Common to dumped contaminated soil particles.

本発明は上述した従来の問題点に鑑みてなされたものであり、セメント原料などとして再利用するための処理コストを低減して、焼却炉から排出される主灰や飛灰などの焼却灰に含まれる塩素を効率的に除去することができる焼却灰の処理方法及び焼却灰の処理設備、並びに、粗大物が混入した粉粒状の処理対象物の処理装置を提供することを目的とする。   This invention is made | formed in view of the conventional problem mentioned above, reduces the processing cost for reusing as a cement raw material etc., and incinerated ash, such as main ash and fly ash discharged | emitted from an incinerator. It aims at providing the processing method of the incineration ash which can remove the chlorine contained efficiently, the processing equipment of the incineration ash, and the processing apparatus of the granular processing object mixed with the coarse thing.

上述の目的を達成するため、本発明による焼却灰の処理方法の特徴構成は、特許請求の範囲の書類の請求項1に記載した通り、焼却灰を洗浄処理する焼却灰の処理方法であって、焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する第一工程と、前記第一工程で分離洗浄された焼却主灰を分級する第二工程を備える点にある。   In order to achieve the above object, the characteristic configuration of the incineration ash processing method according to the present invention is the incineration ash processing method for cleaning the incineration ash as described in claim 1 of the claims. The first step of cleaning the incinerated main ash separated and recovered from the incinerated ash while separating unburned and unsuitable materials, and the second step of classifying the incinerated main ash separated and washed in the first step It is in.

第一工程では、焼却主灰が洗浄される過程で、同時に未燃物や不適物が分離除去され、第二工程では焼却主灰のみが適切に洗浄されるようになる。従って、第二工程に未燃物や不適物が混入することが無くなり、円滑に分級処理を進めることができるようになる。   In the first step, the incinerated main ash is washed, and unburned materials and unsuitable materials are separated and removed at the same time. In the second step, only the incinerated main ash is appropriately washed. Accordingly, unburned materials and unsuitable materials are not mixed in the second step, and the classification process can be smoothly performed.

同第二の特徴構成は、同請求項2に記載した通り、上述の第一特徴構成に加えて、前記焼却灰から分離回収された焼却主灰が、事前に洗浄されることなく、前記第一工程に投入される点にある。   In addition to the first feature configuration described above, the second feature configuration according to claim 2 is the same as the first feature configuration described above, but the incineration main ash separated and recovered from the incineration ash is not cleaned in advance. The point is that it is put into one process.

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特徴構成に加えて、前記第一工程は、洗浄水が充填された洗浄槽に焼却主灰を投入して、洗浄水に浮遊する未燃物を分離する浮遊物分離工程と、洗浄水に沈降する不適物を除去する不適物除去工程と、浮遊物及び不適物が除去された焼却主灰を後段の分級工程に搬送する搬送工程とを備えている点にある。   In the third feature configuration, in addition to the first or second feature configuration described above, the first step is to put incinerated main ash into a cleaning tank filled with cleaning water. Then, the floating substance separation process for separating unburned substances floating in the washing water, the unsuitable substance removal process for removing unsuitable substances that settle in the washing water, and the incineration main ash from which the floating substances and unsuitable substances have been removed And a transporting process for transporting to the classifying process.

同第四の特徴構成は、同請求項4に記載した通り、前記第一工程は、充填された洗浄水が上下に脈動する脈動洗浄槽に投入された焼却主灰を洗浄しながら、比重差によって焼却主灰に含まれる未燃物を浮遊させて上層の洗浄水とともに搬出する浮遊物分離工程と、比重差によって洗浄水に沈降する不適物を受け止めて搬出する不適物除去工程と、底部に沈降する焼却主灰を後段の分級工程に搬送する搬送工程を備えている点にある。   In the fourth feature configuration, as described in claim 4, the first step is performed while cleaning the incinerated main ash charged in the pulsation washing tank in which the filled washing water pulsates up and down, and the specific gravity difference Floating substance separation process that floats unburned material contained in the incineration main ash and transports it with the upper washing water, unsuitable substance removal process that accepts and transports unsuitable substances that settle in the washing water due to the difference in specific gravity, and It is in the point provided with the conveyance process which conveys the incineration main ash which settles to a subsequent classification process.

同第五の特徴構成は、同請求項5に記載した通り、焼却灰を洗浄処理する焼却灰の処理方法であって、焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する洗浄工程と、洗浄工程後の焼却主灰を予め複数段に設定された基準粒径に基づいて分級する分級工程と、分級工程後の小径側の焼却主灰を再洗浄する再洗浄工程とを備え、洗浄工程後の焼却主灰に対して前記基準粒径が大から小なる順に前記分級工程と前記再洗浄工程を繰り返す点にある。   The fifth characteristic configuration is the incineration ash treatment method for cleaning the incineration ash as described in claim 5, wherein the incineration main ash separated and recovered from the incineration ash is treated with unburned or unsuitable materials. A cleaning process for cleaning while separating, a classification process for classifying the incinerated main ash after the cleaning process based on a standard particle size set in advance in multiple stages, and a reinspection of the incinerated main ash on the small diameter side after the classification process A re-washing step, and the classification step and the re-washing step are repeated in order from the largest to the smallest particle size of the incinerated main ash after the washing step.

本願発明者は、鋭意研究を重ねた結果、焼却主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ことが判明した。即ち、図4に示すように、焼却主灰の粒径の違いにより塩素の含有量が大きく異なり、塩素含有量に基づいて粒径2mm以上の粗粒灰と、粒径0.15mm〜2mmの細粒灰と、0.15mmより小径の微粒灰に分類し、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できるという新知見を得ることができた。上述の構成によれば、塩素含有率に基づいて複数段に設定された基準粒径に基づいて焼却灰を多段に分級することにより、比較的塩素含有量の少ない大径の粒子は少量の洗浄水で十分に脱塩素処理しながら、塩素含有量の多い粒径の小さい焼却灰ほど多段階に洗浄することができる。しかも焼却主灰を対象に洗浄処理するものであり、塩素含有率の高い焼却飛灰を同時に洗浄処理するものではないため、少ない洗浄水量で効果的に脱塩素処理が行なえ、処理コストを下げることができるのである。   The inventor of the present application has conducted extensive research and found that the incinerated main ash has a different chlorine content depending on the particle size, and the smaller the particle size, the higher the chlorine content. That is, as shown in FIG. 4, the chlorine content varies greatly depending on the particle size of the incinerated main ash, the coarse ash having a particle size of 2 mm or more based on the chlorine content, and the particle size of 0.15 mm to 2 mm. It was classified into fine ash and fine ash with a diameter smaller than 0.15 mm, and new knowledge was obtained that dechlorination could be performed efficiently by changing the cleaning conditions. According to the above-described configuration, the incinerated ash is classified in multiple stages based on the reference particle size set in multiple stages based on the chlorine content, so that large-diameter particles having a relatively small chlorine content are washed in a small amount. Incinerated ash with a large chlorine content and a small particle size can be washed in multiple stages while being sufficiently dechlorinated with water. In addition, the main ash for incineration is washed, and the incineration fly ash with a high chlorine content is not washed at the same time, so the dechlorination treatment can be performed effectively with a small amount of washing water, reducing the treatment cost. Can do it.

同第六の特徴構成は、同請求項6に記載した通り、上述の第五特徴構成に加えて、前記洗浄工程は、洗浄水が充填された洗浄槽に焼却主灰を投入して、浮遊する未燃物を分離する浮遊物分離工程と、沈降する不適物を除去する不適物除去工程と、浮遊物及び不適物が除去された焼却主灰を後段の分級工程に搬送する搬送工程と、前記洗浄槽に洗浄水を補充する洗浄水補充工程を備えている点にある。   In addition to the fifth feature configuration described above, the sixth feature configuration is the same as the fifth feature configuration described above, wherein the cleaning step is performed by injecting incinerated main ash into a cleaning tank filled with cleaning water, and A floating substance separation process for separating unburned substances, an unsuitable substance removal process for removing unsuitable substances that settle, a conveying process for conveying the incinerated main ash from which floating substances and unsuitable substances have been removed to a subsequent classification process, A cleaning water replenishing step of replenishing the cleaning tank with cleaning water is provided.

洗浄槽に投入された焼却主灰に含まれる紙や木片などの未燃物が浮遊物分離工程で除去され、不適物除去工程で大径の金属類やガラ類が除去された主灰は槽内で洗浄され、搬送工程で洗浄水とともに後段の分級工程に搬送される。搬送工程で槽内の洗浄水の一部を排水するとともに、洗浄水補充工程により洗浄水を補充することにより、洗浄槽内で溶解した塩素によりその濃度が飽和に到るようなことを回避して、洗浄性能を維持することができるのである。   The main ash from which unburned materials such as paper and wood chips contained in the incinerated main ash put into the cleaning tank are removed in the floating substance separation process, and large-diameter metals and glass are removed in the unsuitable substance removal process It is washed in the inside, and is conveyed to the subsequent classification step together with the washing water in the conveyance step. By draining a part of the washing water in the tank in the transport process and replenishing the washing water in the washing water replenishment process, it is possible to avoid the concentration of the chlorine reaching saturation due to the dissolved chlorine in the washing tank. Thus, the cleaning performance can be maintained.

同第七の特徴構成は、同請求項7に記載した通り、上述の第六特徴構成に加えて、前記不適物除去工程で除去された不適物に対して金属を除去した後に破砕処理し、被破砕処理物を前記洗浄工程に投入する点にある。   In addition to the sixth feature configuration described above, the seventh feature configuration is crushed after removing the metal from the unsuitable matter removed in the unsuitable matter removing step, as described in claim 7. It exists in the point which throws in to-be-crushed processed material in the said washing | cleaning process.

上述の構成によれば、前記不適物を破砕処理し洗浄工程に投入することで、前記焼却主灰の再利用率を上げることができる。   According to the above-mentioned composition, the recycle rate of the incineration main ash can be raised by crushing the unsuitable thing and throwing it into the washing process.

本発明による焼却灰の処理設備の第一の特徴構成は、同請求項8に記載した通り、焼却灰を洗浄処理する焼却灰の処理設備であって、焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する洗浄装置と、洗浄後の焼却主灰を分級する分級装置とを備えて構成される点にある。   The first characteristic configuration of the incineration ash treatment facility according to the present invention is the incineration ash treatment facility for cleaning the incineration ash as described in claim 8, wherein the incineration main ash separated and recovered from the incineration ash In the point which comprises the washing | cleaning apparatus which isolate | separates unburned material and unsuitable thing, and the classification apparatus which classifies the incinerator main ash after washing | cleaning.

同第二の特徴構成は、同請求項9に記載した通り、前記洗浄装置が、洗浄水が充填され、上部が二つに分岐し下部が連結された管形状の脈動洗浄槽と、前記脈動洗浄槽内の洗浄水を脈動させる脈動発生装置と、前記脈動洗浄槽に投入された焼却主灰を洗浄しながら、比重差によって焼却主灰に含まれる未燃物を浮遊させて上層の洗浄水とともに搬出する排出口と、比重差によって洗浄水に沈降する不適物を受け止めて搬出するコンベア装置と、底部に沈降する焼却主灰を後段の分級工程に搬送するコンベア装置を備えている点にある。   In the second characteristic configuration, as described in claim 9, the cleaning device is filled with cleaning water, has a tubular pulsating cleaning tank in which an upper part is branched into two and a lower part is connected, and the pulsating A pulsation generator that pulsates the cleaning water in the cleaning tank, and the upper cleaning water by floating unburned substances contained in the incinerated main ash due to the difference in specific gravity while cleaning the incinerated main ash charged into the pulsating cleaning tank And a discharge device for carrying out, a conveyor device for receiving and carrying out unsuitable objects that settle in the washing water due to the difference in specific gravity, and a conveyor device for carrying the incinerated main ash settling to the bottom to the subsequent classification process. .

同第三の特徴構成は、同請求項10に記載した通り、焼却灰を洗浄処理する焼却灰の処理設備であって、焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する洗浄装置と、洗浄後の焼却主灰を予め複数段に設定された基準粒径に基づいて大から小なる順に分級する複数の分級装置と、各分級装置の後段に設置され、小径側に分級された焼却主灰を再洗浄する複数の再洗浄装置と、前記再洗浄装置で再洗浄された焼却主灰を脱水処理する脱水装置を備えて構成される点にある。   The third characteristic configuration is an incineration ash treatment facility for cleaning incineration ash as described in claim 10, wherein the incineration main ash separated and recovered from the incineration ash is treated with unburned or unsuitable materials. Installed in the rear stage of each classifier, and a classifier that classifies the incinerated main ash after cleaning based on the standard particle size set in multiple stages in order from large to small. A plurality of re-cleaning devices for re-cleaning the incinerated main ash classified to the small diameter side and a dehydrating device for dehydrating the incinerated main ash re-washed by the re-cleaning device are provided.

上述の構成によれば、前記焼却主灰を塩素含有率の高い粒径の主灰ほど多段に再洗浄されるため、粒径の大きな主灰から粒径の小さな主灰まで効率的に洗浄でき、再利用率を高めることができるようになるのである。   According to the configuration described above, the incinerated main ash is rewashed in multiple stages as the main ash having a higher chlorine content, so that the main ash having a larger particle size can be efficiently cleaned from the main ash having a smaller particle size. It is possible to increase the reuse rate.

同第四の特徴構成は、同請求項11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、前記洗浄装置は、洗浄水が充填された洗浄槽と、前記洗浄槽に充填された洗浄水を脈動させる加振機構と、前記洗浄槽に投入された焼却主灰から浮遊する未燃物を分離する浮遊物分離機構と、沈降する不適物を除去する不適物除去機構と、浮遊物及び不適物が除去され、底部に沈殿した焼却主灰を後段の分級装置に搬送する搬送機構と、洗浄水を前記洗浄槽に補充する洗浄水補充機構を備えたジグ選別装置で構成されている点にある。   In the fourth feature configuration, as described in claim 11, in addition to any one of the first to third feature configurations described above, the cleaning device includes a cleaning tank filled with cleaning water, An oscillating mechanism for pulsating the washing water filled in the washing tank, a floating substance separation mechanism for separating unburned substances floating from the incinerated main ash charged in the washing tank, and an unsuitable thing for removing unsuitable substances that settle. Jig sorting equipped with a removal mechanism, a transport mechanism that transports the incinerated main ash that has been removed from floating and unsuitable materials and settled to the bottom to a subsequent classifier, and a cleaning water replenishment mechanism that replenishes the cleaning tank with cleaning water It is in that it is composed of devices.

上述の構成によれば、槽内の洗浄水が加振機構により脈動されることにより、投入された焼却主灰が洗浄水に効果的に分散されて洗浄されるようになる。そして、焼却主灰に含まれる紙や木片などの未燃物が浮遊物分離機構により除去され、不適物除去機構により大径の金属類やガラ類が除去された主灰はさらに槽内で洗浄されながら槽内に沈殿し、搬送機構により後段の分級装置に搬送される。このとき、洗浄水の一部が搬送機構により排水され、洗浄水補充機構により新たな洗浄水が補充されるため、洗浄槽内で溶解した塩素によりその濃度が飽和に到るようなことが回避され、洗浄性能が維持されるのである。   According to the above-described configuration, the wash water in the tank is pulsated by the vibration mechanism, so that the incinerated main ash that has been thrown in is effectively dispersed and washed in the wash water. Then, unburned materials such as paper and wood chips contained in the incinerated main ash are removed by the floating substance separation mechanism, and the main ash from which large-sized metals and glass are removed by the inappropriate material removal mechanism is further washed in the tank. As it is, it settles in the tank and is transported to the subsequent classifier by the transport mechanism. At this time, a part of the cleaning water is drained by the transport mechanism, and new cleaning water is replenished by the cleaning water replenishment mechanism, so that the concentration of chlorine in the cleaning tank is not saturated. As a result, the cleaning performance is maintained.

同第五の特徴構成は、同請求項12記載した通り、上述の第一から第四の何れかの特徴構成に加えて、前記洗浄装置に形成された焼却主灰の投入部がゴミ焼却炉の灰シュート下部に設けられ、炉内で焼却処理され前記灰シュートから落下した焼却主灰が投入される点にある。   In the fifth feature configuration, in addition to any one of the first to fourth feature configurations described above, the incinerator main ash charging portion formed in the cleaning device is a garbage incinerator. The incinerator main ash which is provided in the lower part of the ash chute and incinerated in the furnace and dropped from the ash chute is charged.

上述の構成によれば、炉内で焼却処理され、灰シュートから落下する焼却主灰がその場で選別、洗浄処理されるため、焼却灰の処理設備が遠方にある場合であっても、無駄な搬送コストを削減することができるようになるのである。例えば、分離された未燃物はその場で再度焼却処理できるのであり、大径の金属類やガラ類を無駄に焼却灰の処理設備まで運搬する必要が無くなるのである。また、焼却主灰中の塩素分がフリーデル氏塩を形成する前に、脱塩素処理が行なわれるため、より少ない洗浄水あるいはより短い洗浄時間で脱塩素処理が可能である。   According to the above-described configuration, the incineration main ash that is incinerated in the furnace and falls from the ash chute is sorted and cleaned on the spot, so even if the incineration ash treatment facility is far away, it is useless. This makes it possible to reduce the cost of transport. For example, the separated unburned material can be incinerated again on the spot, eliminating the need to transport large-diameter metals and glass to waste incineration ash processing equipment. Further, since the dechlorination treatment is performed before the chlorine content in the incinerated main ash forms Friedel's salt, the dechlorination treatment can be performed with less washing water or a shorter washing time.

本発明による処理設備の特徴構成は、同請求項13に記載した通り、粗大物が混入した粉粒状の処理対象物を洗浄処理する処理設備であって、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洗浄装置と、前記洗浄装置で分離洗浄された粉粒体を分級する分級装置とを備えて構成される点にある。   The characteristic configuration of the processing facility according to the present invention is a processing facility for cleaning a granular processing object mixed with a coarse material as described in claim 13, wherein the processing object is cleaned while the processing object is being cleaned. A cleaning device for sorting into powder particles and a classification device for classifying the powder particles separated and washed by the cleaning device are provided.

以上説明した通り、本発明によれば、セメント原料などとして再利用するための処理コストを低減して、焼却炉から排出される主灰や飛灰などの焼却灰に含まれる塩素を効率的に除去することができる焼却灰の処理方法及び焼却灰の処理設備、並びに粗大物が混入した粉粒状の処理対象物を処理する処理設備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, the processing cost for reusing as a cement raw material is reduced, and chlorine contained in incineration ash such as main ash and fly ash discharged from the incinerator is efficiently obtained. An incineration ash processing method and incineration ash processing equipment that can be removed, and a processing equipment for processing a granular processing object mixed with a coarse product can be provided.

以下に、ゴミ焼却設備に併設された焼却灰の処理設備について説明する。図1に示すように、ゴミ焼却設備は、回収されたごみを集積するゴミピット1と、ゴミを焼却処理する炉本体Aと、前記炉本体Aで発生した燃焼排ガスを処理する排ガス処理設備Bなどを備えて構成される。   The incineration ash treatment facility attached to the garbage incineration facility will be described below. As shown in FIG. 1, the waste incineration facility includes a waste pit 1 for collecting collected garbage, a furnace body A for incinerating waste, an exhaust gas treatment equipment B for treating combustion exhaust gas generated in the furnace body A, and the like. It is configured with.

前記炉本体Aは、前記ゴミピット1の天井部に設置されたクレーン装置2のバケット2Aにより把持されたゴミが投入されるホッパー3と、前記ホッパー3に投入されたゴミを炉内に押出し投入するプッシャ4と、投入されたゴミを搬送しながら焼却するストーカ式の焼却処理帯16を備え、焼却された残渣が灰シュート17から落下するように構成されている。   The furnace main body A pushes and throws in the furnace the hopper 3 into which the trash held by the bucket 2A of the crane apparatus 2 installed on the ceiling portion of the trash pit 1 is put, and the trash put into the hopper 3 into the furnace. A pusher 4 and a stoker-type incineration treatment zone 16 that incinerates the introduced garbage while being conveyed are provided, and the incinerated residue is configured to fall from the ash chute 17.

前記排ガス処理設備Bは、炉内で発生した排ガスの熱を回収する廃熱ボイラ7と、排ガスに含まれる硫黄酸化物を無害化する接触脱硫装置や有毒成分を吸着する活性炭吸着塔や煤塵などを取り除くバグフィルタなどで構成される排ガス処理機構11などを備えて構成され、前記排ガス処理機構11により分離された固形物が焼却飛灰として回収される。さらに、前記廃熱ボイラ7から供給される蒸気で駆動される蒸気タービン8により発電する発電機9と、前記蒸気タービン8から送られる水(復水)を加熱して廃熱ボイラ7に戻すよう煙道に送られたエコノマイザ10などを備え、前記排ガス処理設備Bで浄化された排ガスは誘引送風機12により誘引されて煙突13から排気される。   The exhaust gas treatment facility B includes a waste heat boiler 7 that recovers heat of exhaust gas generated in the furnace, a catalytic desulfurization device that renders sulfur oxides contained in the exhaust gas harmless, an activated carbon adsorption tower that adsorbs toxic components, dust, etc. The solid matter separated by the exhaust gas treatment mechanism 11 is collected as incineration fly ash. Furthermore, the generator 9 that generates power by the steam turbine 8 driven by the steam supplied from the waste heat boiler 7 and the water (condensate) sent from the steam turbine 8 are heated and returned to the waste heat boiler 7. The economizer 10 and the like sent to the flue are provided, and the exhaust gas purified by the exhaust gas treatment facility B is attracted by the induction blower 12 and exhausted from the chimney 13.

焼却灰の処理設備は、図3に示すように、粒径200mm以下の焼却主灰を未燃物や不適物を分離選別しながら洗浄する洗浄装置としてのジグ選別装置18と、洗浄された焼却主灰から予め塩素含有率に基づいて複数段に設定された基準粒径に基づいて大から小なる順に焼却主灰を分級する第一及び第二分級装置24、40と、各分級装置24、40の後段に設置され、小径側に分級された焼却主灰を再洗浄する第一及び第二再洗浄装置41、42と、第二再洗浄装置44で再洗浄された焼却主灰をリンス水で濯いで脱水処理する第一脱水装置45と、第二分級装置40で大径側に分級された微粒灰を沈降させる灰沈降槽42と、前記排ガス処理機構11から回収された焼却飛灰を洗浄水と混合してスラリー化するスラリー化装置46と、スラリー化された焼却飛灰を脱水処理する第二脱水装置47などを備えて構成されている。   As shown in FIG. 3, the incineration ash treatment equipment includes a jig sorting device 18 as a washing device for washing incineration main ash having a particle size of 200 mm or less while separating unsorted and unsuitable materials, and a washed incineration. First and second classifiers 24 and 40 for classifying incinerated main ash from the main ash in advance from the largest to the smallest based on the reference particle size set in multiple stages based on the chlorine content, and each classifier 24, First and second re-cleaning devices 41 and 42 for re-cleaning the incinerated main ash classified on the small-diameter side and the incinerated main ash re-washed by the second re-cleaning device 44 are rinsed water. The first dewatering device 45 that is rinsed and dewatered in the ash, the ash sedimentation tank 42 that settles the fine ash classified on the large diameter side by the second classifying device 40, and the incineration fly ash recovered from the exhaust gas treatment mechanism 11 A slurrying device 46 for mixing with washing water to form a slurry; And it is configured to Lee reduction has been incineration fly ash and the like second dewatering device 47 for dewatering.

図4は、焼却主灰を、メッシュ幅4.75mm、2mm、1mm、0.3mm、0.15mmで篩分けして、夫々に散水した後の塩素の含有量を分析した値である。図より、粒径2mm以上の粗粒灰では、簡易な洗浄処理のみでセメント原料として十分に使用できる1000mg/Kg以下に塩素が除去されていること、粒径0.15mm〜2mmの微粒灰では塩素含有量が1600〜2000mg/Kgとほぼ同じであること、0.15mmより小径の微粒灰は3000mg/Kgであり、粒径0.15mm〜2mmの微粒灰より塩素含有量が多いことが理解される。尚、主灰の粒径に対する塩素含有量の分布はゴミ焼却炉で焼却処理されるゴミの性状により多少の差異があり、そのような場合には、予め粒径毎の塩素含有量を分析することにより分級サイズを脱塩に適したサイズに調整する必要がある。   FIG. 4 is a value obtained by analyzing the content of chlorine after sieving the incinerated main ash with a mesh width of 4.75 mm, 2 mm, 1 mm, 0.3 mm, and 0.15 mm and sprinkling water. From the figure, in coarse ash with a particle size of 2 mm or more, chlorine is removed to 1000 mg / Kg or less that can be sufficiently used as a cement raw material only by simple cleaning treatment, and for fine ash with a particle size of 0.15 mm to 2 mm It is understood that the chlorine content is almost the same as 1600 to 2000 mg / Kg, the fine ash having a diameter smaller than 0.15 mm is 3000 mg / Kg, and the chlorine content is larger than the fine ash having a particle diameter of 0.15 mm to 2 mm. Is done. In addition, the distribution of the chlorine content with respect to the particle size of the main ash has some differences depending on the properties of the waste incinerated in the waste incinerator. In such a case, the chlorine content for each particle size is analyzed in advance. Therefore, it is necessary to adjust the classification size to a size suitable for desalting.

前記ジグ選別装置18は、図2に示すように、洗浄水が充填されたU字管で構成された洗浄槽20と、前記洗浄槽20に充填された洗浄水を脈動させる加振機構21と、前記洗浄槽20に投入された焼却主灰から浮遊物を分離する浮遊物分離機構22と、不適物として最大基準粒径より大径の金属類やガラ類を除去する不適物除去機構23と、浮遊物及び不適物が除去され、底部に沈殿した焼却主灰を洗浄水とともに後段の第一分級装置24に搬送するバケット式の搬送機構25と、前記搬送機構25による搬送処理で減量した洗浄水を前記洗浄槽20に補充する洗浄水補充機構26を備えて構成され、前記洗浄槽20への焼却主灰の投入部が前記焼却炉の灰シュート17の下方に設けられている。   As shown in FIG. 2, the jig sorting device 18 includes a cleaning tank 20 composed of a U-shaped tube filled with cleaning water, and a vibration mechanism 21 that pulsates the cleaning water filled in the cleaning tank 20. A floating substance separation mechanism 22 that separates floating substances from the incinerated main ash charged into the washing tank 20, and an inappropriate substance removal mechanism 23 that removes metals and glass larger than the maximum reference particle size as inappropriate substances. The bucket-type transport mechanism 25 that transports the incinerated main ash that has been removed from the floating and unsuitable materials and settled to the bottom together with the cleaning water to the first classifier 24, and the cleaning that has been reduced in the transport process by the transport mechanism 25 A washing water replenishing mechanism 26 for replenishing the washing tank 20 with water is provided, and a charging portion of the incinerated main ash to the washing tank 20 is provided below the ash chute 17 of the incinerator.

前記加振機構21は、U字管の一端に配置され、モータ27と、前記モータ27に連結された回転盤28と、前記回転盤28にピストン29を介して接続された水振板30とで構成されている。前記モータ27の駆動により前記回転盤28が回転することにより、前記ピストン29を介して接続された前記水振板30が上下することで前記洗浄槽20の一端の水面を上下させ、前記洗浄槽20の洗浄水を脈動させる。洗浄水の水面を脈動させることで、前記洗浄槽20に投入された浮遊物及び不適物を含む焼却主灰を槽内で分散させて洗浄する洗浄工程を行いながら浮遊物及び不適物の除去を行う。   The vibration mechanism 21 is disposed at one end of a U-shaped tube, and includes a motor 27, a rotating plate 28 connected to the motor 27, and a water vibrating plate 30 connected to the rotating plate 28 via a piston 29. It consists of When the rotating disk 28 is rotated by driving the motor 27, the water vibration plate 30 connected via the piston 29 is moved up and down to raise and lower the water surface at one end of the washing tank 20, thereby Pulsate 20 wash water. By pulsating the surface of the washing water, the floating ash and unsuitable substances are removed while performing a washing process in which the incinerated main ash containing the floating substances and unsuitable substances put into the washing tank 20 is dispersed and washed in the tank. Do.

前記浮遊物分離機構22は、前記洗浄槽20の他端側部に設けられた浮遊物排出口31と、前記浮遊物排出口31より排出された木片や紙類などの未燃状態の浮遊物を回収する浮遊物回収部32とで構成され、浮遊物は前記加振機構21によって脈動する洗浄水により前記浮遊物排出口31からオーバーフロー水とともに排出され、前記浮遊物回収部32に回収される。前記浮遊物回収部32で洗浄水と分離された浮遊物は前記焼却炉で再処理すべく前記ゴミピット1に戻され、洗浄水はポンプ33と洗浄水管34を備えた洗浄水回収機構19により前記洗浄槽20へ回収される。   The floating substance separation mechanism 22 includes a floating substance discharge port 31 provided at the other end side of the cleaning tank 20 and unburned floating substances such as wood pieces and paper discharged from the floating substance discharge port 31. The floating substance is discharged from the floating substance discharge port 31 together with the overflow water by the washing water pulsated by the vibration mechanism 21 and is collected by the floating substance collecting part 32. . The suspended matter separated from the washing water in the floating matter collecting unit 32 is returned to the garbage pit 1 to be reprocessed in the incinerator, and the washing water is returned by the washing water collecting mechanism 19 having a pump 33 and a washing water pipe 34. It is collected in the cleaning tank 20.

前記不適物除去機構23は、一部が前記洗浄槽20の洗浄水中を通過するように配置されたメッシュコンベア機構35で構成され、洗浄槽20に投入され、メッシュコンベア上に沈降する焼却主灰のうちその網目より小さい粒径の焼却主灰がそのまま沈降し、大きい粒径の不適物が前記メッシュコンベアにより槽外に搬送除去される。前記メッシュコンベア機構35により、例えば10mm以上の粒径の金属類やガラなどの不適物が除去され、金属回収機構36aにより金属類が除去されたガラは、破砕装置36bによって破砕され、焼却主灰として再びジグ選別装置18に投入される。   The inadequate material removal mechanism 23 is composed of a mesh conveyor mechanism 35 that is arranged so that a part thereof passes through the cleaning water of the cleaning tank 20, and is put into the cleaning tank 20 and incinerated main ash that settles on the mesh conveyor. Among them, the incinerated main ash having a particle size smaller than that of the mesh settles as it is, and unsuitable materials having a large particle size are conveyed and removed out of the tank by the mesh conveyor. The mesh conveyor mechanism 35 removes unsuitable materials such as metals and glass having a particle size of 10 mm or more, and the metal from which the metals have been removed by the metal recovery mechanism 36a is crushed by the crushing device 36b and incinerated main ash As shown in FIG.

前記搬送機構25は、側部に複数の小径の開口を形成したバケット37が無限軌道に沿って複数並設されたバケットコンベア機構38で構成され、前記洗浄槽20の底部に沈降堆積した焼却主灰を洗浄水とともにバケット37で掻き出して、前記第一分級装置24へ運搬する。尚、前記開口の孔径や開孔率を適切な値に設定することにより、持ち出される洗浄水の量と補充される洗浄水の量が調整される。   The transport mechanism 25 is composed of a bucket conveyor mechanism 38 in which a plurality of buckets 37 each having a plurality of small-diameter openings are arranged along an endless track, and an incinerator main body settled and deposited on the bottom of the cleaning tank 20. The ash is scraped out together with the washing water by the bucket 37 and conveyed to the first classifier 24. In addition, the amount of the wash water taken out and the amount of the wash water to be replenished are adjusted by setting the hole diameter and the aperture ratio of the opening to appropriate values.

前記第一分級装置24は振動篩装置で構成され、前記ジグ選別装置18で洗浄された10mmより小径の焼却主灰を粒径2mm以上の粗粒灰と粒径2mm未満の第一微粒灰とに分級する。分級された粒径2mm以上の粗粒灰は第一散水装置39へ投入された後、貯留設備において重力によって灰中の自由水が脱水されてセメント原料として回収され、粒径2mm未満の第一微粒灰は第一再洗浄装置41へ投入されて再度洗浄される。   The first classifier 24 is composed of a vibration sieve device, and the incinerated main ash having a diameter smaller than 10 mm washed by the jig sorting device 18 is composed of coarse ash having a particle size of 2 mm or more and first fine ash having a particle size of less than 2 mm. Classify. After the classified coarse ash having a particle size of 2 mm or more is charged into the first watering device 39, free water in the ash is dehydrated by gravity in the storage facility and recovered as a cement raw material. The fine ash is put into the first re-cleaning device 41 and cleaned again.

粗粒灰に含まれる塩素濃度はセメントメーカの受け入れ基準である1000mg/Kg以下を満足しており、さらに洗浄しても塩素含有率が殆ど変化しないため、水やエネルギーの利用効率の観点で洗浄を終了するものである。   The chlorine concentration in the coarse ash satisfies the cement manufacturer's acceptance standard of 1000 mg / Kg or less, and even when washed, the chlorine content hardly changes, so washing is performed from the viewpoint of water and energy utilization efficiency. Is to end.

前記第一再洗浄装置41は、攪拌モータ41aを備えた攪拌装置41bと、洗浄された焼却主灰をポンプ41cを介して第二分級装置40に搬送する灰スラリー搬送管41dを備えて構成され、再洗浄された第一微粒灰は前記第二分級装置40によりさらに分級される。   The first re-cleaning device 41 includes a stirring device 41b including a stirring motor 41a, and an ash slurry transport pipe 41d that transports the cleaned incinerated main ash to the second classifying device 40 via a pump 41c. The re-washed first fine ash is further classified by the second classifier 40.

前記第二分級装置40は湿式サイクロンで構成され、粒径0.15mm〜2mmの第二微粒灰と粒径0.15mm未満の第三微粒灰に分級する。分級された第二微粒灰は、灰沈降槽42で沈降し、掻き出し装置43により排出され、貯留設備において重力によって灰中の自由水が脱水され、セメント原料として回収される。また、分級された第三微粒灰は、第二再洗浄装置44へ投入されて再度洗浄される。第三微粒灰に含まれる塩素の濃度は第二微粒灰の約2倍であり、第三微粒灰をさらに洗浄することにより塩素含有量を低減してセメント原料として有効に再利用できるようになる。   The second classifier 40 is composed of a wet cyclone and classifies it into second fine ash having a particle size of 0.15 mm to 2 mm and third fine ash having a particle size of less than 0.15 mm. The classified second fine ash settles in the ash settling tank 42 and is discharged by the scraping device 43, and free water in the ash is dehydrated by gravity in the storage facility and collected as a cement raw material. Further, the classified third fine ash is supplied to the second re-cleaning device 44 and cleaned again. The concentration of chlorine contained in the third fine ash is about twice that of the second fine ash, and further cleaning of the third fine ash reduces the chlorine content and enables effective reuse as a cement raw material. .

前記第二再洗浄装置44は、攪拌モータ44aを備えた攪拌装置44bと、再洗浄された焼却主灰をポンプ44cを介して第一脱水装置45に搬送する処理水搬送管44dを備えて構成され、再洗浄された第二微粒灰は前記第一脱水装置45で脱水処理された後にセメント原料として回収される。   The second re-cleaning device 44 includes a stirring device 44b having a stirring motor 44a and a treated water transport pipe 44d for transporting the re-washed incinerated main ash to the first dehydrating device 45 through the pump 44c. The re-washed second fine ash is dehydrated by the first dehydrator 45 and then recovered as a cement raw material.

前記第一脱水装置45で生じる濾液は、脱水濾液槽48に貯留され、一部が前記ジグ選別装置18の洗浄水を補充するために使用され、残液は第一水処理装置49へ送られて、カルシウム除去、生物脱窒、凝集沈殿、砂濾過、活性炭濾過などの浄水処理が行われた後に放流される。つまり、脱水濾液槽48に接続されるポンプ48cと前記ジグ選別装置18に繋がる管路により洗浄水補充機構26が構成される。さらに、前記第一散水装置39で使用されたリンス水の濾液等、塩素濃度の低い洗浄廃水も洗浄水補充機構26により前記ジグ選別装置18に返送されて再利用される。   The filtrate produced in the first dehydrator 45 is stored in a dehydrated filtrate tank 48, a part of which is used to replenish the washing water of the jig sorting device 18, and the remaining liquid is sent to the first water treatment device 49. Then, it is discharged after water purification treatment such as calcium removal, biological denitrification, coagulation sedimentation, sand filtration and activated carbon filtration. That is, the washing water replenishing mechanism 26 is constituted by the pump 48 c connected to the dehydrated filtrate tank 48 and the pipe line connected to the jig sorting device 18. Further, washing wastewater having a low chlorine concentration, such as the rinse water filtrate used in the first watering device 39, is returned to the jig sorting device 18 by the washing water replenishing mechanism 26 and reused.

前記排ガス処理機構11から回収された飛灰は、スラリー化装置46に投入されて洗浄された後に第二脱水装置47へ送られる。スラリー化された焼却飛灰は、第二脱水装置47で脱水処理されセメント原料として回収される。第二脱水装置47からの濾液は処理水槽50に貯留され、第二水処理装置51でカルシウム除去、砂濾過、活性炭などの浄水処理が行われた後に放流される。   The fly ash collected from the exhaust gas treatment mechanism 11 is fed into the slurrying device 46 and washed, and then sent to the second dehydrating device 47. The slurried incineration fly ash is dehydrated by the second dehydrator 47 and recovered as a cement raw material. The filtrate from the second dehydrator 47 is stored in the treated water tank 50 and discharged after the second water treatment device 51 performs water removal treatment such as calcium removal, sand filtration, and activated carbon.

以上説明した通り、前記ジグ選別装置18により焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する洗浄工程が実行され、洗浄後の焼却主灰から予め塩素含有率に基づいて複数段に設定された基準粒径に基づいて大径の焼却主灰を分級する分級工程が前記第一及び第二分級装置24、40で実行され、残余の小径の焼却主灰を再洗浄する再洗浄工程が前記第一及び第二再洗浄装置41、44で実行され、洗浄後の焼却主灰に対して前記基準粒径が大から小なる順に前記分級工程と前記再洗浄工程が繰り返されるように構成されている。   As described above, a cleaning process for cleaning the incinerated main ash separated and recovered from the incinerated ash by the jig sorting apparatus 18 while separating unburned and unsuitable materials is performed, and chlorine is previously contained in the incinerated main ash after cleaning. A classifying step for classifying large-diameter incineration main ash based on the reference particle size set in a plurality of stages based on the rate is performed in the first and second classifiers 24 and 40, and the remaining small-diameter incineration main ash The re-washing process for re-washing is performed by the first and second re-washing devices 41 and 44, and the classification step and the re-washing are performed in order from the largest to the smallest particle size with respect to the incinerated main ash after washing. It is comprised so that a process may be repeated.

以下に本発明の別実施形態を説明する。上述した実施形態では、焼却灰の処理設備がゴミ焼却設備に併設された例を示し、焼却炉の灰シュート17から落下する焼却主灰を直接にジグ選別装置18に投入することができるように構成したものを説明したが、灰シュート17から水封コンベアに落下し、灰ピットに回収された焼却主灰をジグ選別装置18に投入するように構成するものであってもよい。また、焼却灰の処理設備は、ゴミ焼却設備の敷地とは離隔した地域に構築されるものであってもよい。   Another embodiment of the present invention will be described below. In the above-described embodiment, an example in which the incineration ash treatment facility is provided in the waste incineration facility is shown so that the incineration main ash falling from the ash chute 17 of the incinerator can be directly input to the jig sorting device 18. Although what was comprised was demonstrated, you may comprise so that the incineration main ash which falls to the water-sealed conveyor from the ash chute | shoot 17 and was collect | recovered by the ash pit may be thrown into the jig | tool sorter 18. FIG. The incineration ash treatment facility may be constructed in an area separated from the site of the waste incineration facility.

上述の実施形態では、粗大物が混入した粉粒状の処理対象物である焼却主灰を、直接ジグ選別装置に投入する例を説明したが、ジグ選別装置に投入する前に焼却主灰から粗大物を分離除去した後にジグ選別装置に投入するように構成してもよく、粗大物を除去した後に、焼却主灰に混入している金属類を磁選機にかけて回収するように構成してもよい。焼却主灰には、自転車、鍋、釜等の粗大物が混入している場合もあり、そのような場合には、ジグ選別装置を円滑に運転することが困難な場合もあるからである。   In the above-described embodiment, the incineration main ash, which is a granular processing object mixed with a coarse material, has been described as being directly input into the jig sorting apparatus. However, before being put into the jig sorting apparatus, the incineration main ash is coarse from the incinerated main ash. It may be configured to be put into a jig sorter after separating and removing the material, or after removing the coarse material, the metal mixed in the incinerated main ash may be collected using a magnetic separator. . This is because the incinerator main ash may be mixed with coarse items such as bicycles, pans, and kettles, and in such cases, it may be difficult to operate the jig sorting device smoothly.

粗大物を分離除去する場合には、粗大物の流れの方向に沿って、フレームに鋼製バーを一定の間隔で下流側が傾斜する姿勢で配列し、加振機によりフレームまたは鋼製バーを振動させるグリズリー振動フィーダを用いることができる。   When separating and removing coarse materials, arrange steel bars on the frame in a posture that the downstream side is inclined at regular intervals along the direction of flow of the coarse materials, and the frame or steel bar is vibrated by a vibrator. A grizzly vibratory feeder can be used.

上述の実施形態では、ジグ選別装置を用いて、焼却主灰から未燃物や不適物を分離しながら洗浄する洗浄工程が実行された後、複数段の分級工程で分級処理する例を説明したが、本発明による焼却灰の処理方法は、焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する第一工程と、前記第一工程で分離洗浄された焼却主灰を分級する第二工程を備えるものであればよく、第二工程が複数段の分級工程を備えるものに限らず、一段の分級工程のみを備えるものであってもよい。このような処理方法により、第二工程に未燃物や不適物が混入することが無くなり、円滑に分級処理を進めることができるようになる。   In the above-described embodiment, an example in which a classification process is performed in a multi-stage classification process after the cleaning process of separating unburned and unsuitable substances from the incinerated main ash is performed using the jig sorting apparatus has been described. However, the method for treating incineration ash according to the present invention includes a first step of washing the incinerated main ash separated and recovered from the incineration ash while separating unburned and unsuitable materials, and the incineration separated and washed in the first step. What is necessary is just to have the 2nd process which classifies main ash, and the 2nd process is not restricted to what has a plurality of classification processes, and may have only one classification process. By such a processing method, unburned materials and unsuitable materials are not mixed in the second step, and the classification process can be smoothly performed.

また、一段の分級工程に用いられる分級装置の構成は、特に制限されるものではなく、振動篩装置、湿式サイクロン、流水式分級機等、適宜公知の分級装置を用いることができる。   Moreover, the structure of the classification apparatus used for a one-stage classification process is not specifically limited, A well-known classification apparatus, such as a vibration sieve apparatus, a wet cyclone, a flowing water classifier, can be used suitably.

上述した実施形態では、焼却主灰を粒径により三つに分類したが、これに限るものではなく、焼却主灰によっては二つあるいは四つ以上に分類し、夫々について分級工程と再洗浄工程を行なうことも可能である。   In the embodiment described above, the incinerated main ash is classified into three according to the particle size, but is not limited to this, and depending on the incinerated main ash, it is classified into two or four or more, and a classification process and a re-cleaning process for each. It is also possible to perform.

上述した実施形態では、前記洗浄装置にジグ選別装置を用いたが、これに限るものではなく、焼却主灰から浮遊物及び不適物を除去するものであれば、ジグ選別装置以外の選別装置を用いることも可能である。   In the above-described embodiment, a jig sorting device is used as the cleaning device. However, the present invention is not limited to this, and a sorting device other than the jig sorting device may be used as long as it removes suspended matter and inappropriate materials from the incinerated main ash. It is also possible to use it.

以下に、上述したジグ選別装置とは構成が異なるジグ選別装置を用いた焼却灰の処理方法及び処理設備を説明する。   Below, the processing method and processing equipment of the incineration ash using the jig sorter whose composition differs from the jig sorter mentioned above are explained.

図8に示すように、粉粒体の処理システム100は、処理対象物である焼却灰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に分級する湿式選別手段200と、湿式選別手段200で分級された微粒物を再洗浄する第一の再洗浄手段400と、湿式選別手段200で分級された中粒物を再洗浄する第二の再洗浄手段600を備えている。   As shown in FIG. 8, the granular material processing system 100 sorts the granular material into a coarse particle and a granular material while washing the incinerated ash that is the object to be processed, and the granular material from the fine particle and the fine particle. Wet-sorting means 200 for classifying medium grains having a large particle size, first re-washing means 400 for re-washing the fine particles classified by the wet-sorting means 200, and re-sorting the intermediate grains classified by the wet-sorting means 200 A second re-cleaning means 600 for cleaning is provided.

さらに、第一の再洗浄手段400から排出された洗浄排水を前記湿式選別手段200へ返送する第一の循環経路800と、第二の再洗浄手段600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900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。   Furthermore, the first waste water discharged from the first re-cleaning means 400 is returned to the wet sorting means 200, and the waste water discharged from the second re-cleaning means 600 is returned to the second re-cleaning means 200. A second circulation path 900 that returns to the cleaning means is provided, and the cleaning wastewater returned through each circulation path is reused as cleaning water.

図5から図7に示すように、湿式選別手段200は、洗浄水が充填され底部が傾斜した平面視矩形の洗浄水槽120と、一方の上部開口が洗浄水槽120と連通し、他方の開口に脈動発生装置130が設けられたU字管形状の脈動洗浄槽121と、脈動洗浄槽121の一方の開口及び洗浄水槽120の傾斜底部に沿って配置され、プーリー122a,122b,122cによって回転支持された網目状の搬送面を備えたコンベアベルト122と、コンベアベルト122の回転方向に沿って複数設けられ、コンベアベルト122の回転方向とは逆方向に向けて水流を形成する水噴射ノズル123a、123b、123c、123dを備えたジグ選別装置で構成されている。   As shown in FIG. 5 to FIG. 7, the wet sorting means 200 includes a washing water tank 120 having a rectangular shape in plan view, filled with washing water and inclined at the bottom, and one upper opening communicating with the washing water tank 120, and the other opening. A U-shaped pulsating washing tank 121 provided with a pulsation generating device 130, one opening of the pulsating washing tank 121 and the inclined bottom of the washing water tank 120, are rotatably supported by pulleys 122a, 122b, 122c. A plurality of conveyor belts 122 having a mesh-like transport surface, and water jet nozzles 123a and 123b that are provided along the rotation direction of the conveyor belt 122 and that form a water flow in a direction opposite to the rotation direction of the conveyor belt 122. , 123c, and 123d.

脈動発生装置130は、脈動洗浄槽121の他方の開口の水面近傍からベローズ137、ロッド132を介してプランジャ131を上下動させるために連結されたエキセントリックシーブ133を備え、エキセントリックシーブ133の回転軸を回転駆動するモータ134を備えている。   The pulsation generator 130 includes an eccentric sheave 133 connected to move the plunger 131 up and down through the bellows 137 and the rod 132 from the vicinity of the water surface of the other opening of the pulsation washing tank 121, and the rotational shaft of the eccentric sheave 133 is provided. A motor 134 that rotates is provided.

インバータ装置によりモータ134の回転数が調整され、モータ134の回転に伴なってベローズ137が伸縮作動されることにより、脈動洗浄槽121を介して洗浄水槽120内の水が上下方向に脈動する。   The number of rotations of the motor 134 is adjusted by the inverter device, and the bellows 137 is expanded and contracted as the motor 134 rotates, so that the water in the cleaning water tank 120 pulsates in the vertical direction via the pulsating cleaning tank 121.

脈動発生装置130は、上下動するプランジャ131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、脈動する液面の高さを変更することができる。   The pulsation generator 130 includes a stroke length adjustment mechanism (not shown) that adjusts the stroke length of the plunger 131 that moves up and down, and can change the height of the pulsating liquid surface.

前記ストローク長調整機構としては、プランジャ131の取付け位置を上下方向に調整する機構、ロッド132の長さを調整する機構、ロッド132のエキセントリックシーブ133に取付ける位置を直径方向に調整する機構を用いることができる。   As the stroke length adjusting mechanism, a mechanism for adjusting the mounting position of the plunger 131 in the vertical direction, a mechanism for adjusting the length of the rod 132, and a mechanism for adjusting the mounting position of the rod 132 on the eccentric sheave 133 in the diametrical direction are used. Can do.

脈動洗浄槽121は、コンベアベルト122の延出方向に沿って三分割され、夫々に異なる偏心位置で回転軸135が取付けられたエキセントリックシーブ133が配され、位相が異なる脈動が付与される。   The pulsation washing tank 121 is divided into three along the extending direction of the conveyor belt 122, and eccentric sheaves 133 to which the rotation shafts 135 are attached at different eccentric positions are arranged, and pulsations with different phases are applied.

ベルトコンベア装置136によって湿式選別手段200に搬送された処理対象物は、振動フィーダ124により洗浄水槽120に投入され、脈動洗浄槽121による洗浄水の上下方向の脈動により分散されて、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)は洗浄水によって付着した灰が除去された後にコンベアベルト122によって粗大物搬出口125から排出され、比重の小さな有機質材(ゴム、プラスチック、紙、繊維、木片等)は水面に浮上して水噴射ノズル123a、123b、123c、123dによる水流に従って溢流堰126から排水樋127に流出する。   The processing object conveyed to the wet sorting means 200 by the belt conveyor device 136 is put into the washing water tank 120 by the vibration feeder 124, dispersed by the vertical pulsation of the washing water by the pulsation washing tank 121, and mixed into the ash. Among the coarse materials, metals and glass having large specific gravity (such as stones and glass pieces) are discharged from the coarse material outlet 125 by the conveyor belt 122 after the ash adhering to the washing water is removed, and organic materials having a small specific gravity ( Rubber, plastic, paper, fiber, wood chips, etc.) float on the water surface and flow out from the overflow weir 126 to the drainage basin 127 according to the water flow by the water injection nozzles 123a, 123b, 123c, 123d.

即ち、湿式選別手段200では、粗大物が、比重差によって粗大物を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比重選別工程が実行される。   That is, in the wet sorting means 200, a specific gravity sorting step is performed in which the coarse product is sorted into a coarse product with a large specific gravity and a coarse product with a low specific gravity by the specific gravity difference.

また、洗浄水槽120に投入された灰は、脈動洗浄槽121による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灰(粗粒灰と細粒灰)は水槽内に沈降し、沈降速度の小さい微粒灰は水噴射ノズル123a、123b、123c、123dによる水流に従って洗浄水中を浮遊して溢流堰126から排水樋127に流出する。   Further, the ash charged into the washing water tank 120 is dispersed by the vertical pulsation of the washing water in the pulsating washing tank 121, and the medium ash (coarse ash) that has a large sedimentation speed and settles against the upward pulsating flow. And fine ash) settles in the water tank, and the fine ash having a low sedimentation velocity floats in the washing water according to the water flow by the water injection nozzles 123a, 123b, 123c, 123d and flows out from the overflow weir 126 to the drainage basin 127.

即ち、湿式選別手段200では、粉粒体である灰が、沈降速度差によって微粒灰と微粒灰より粒径が大きい中粒灰とに分級される分級工程が実行される。   That is, in the wet sorting means 200, a classification step is performed in which the ash that is a granular material is classified into fine ash and medium ash having a larger particle size than the fine ash due to a difference in sedimentation speed.

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。つまり、図9(a)に示すように、粉粒体処理システムは、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二以上の群に分級する。また、図9(b)に示すように、湿式選別手段は、比重差によって粗大物を比重の大きい粗大物と比重の小さい粗大物に選別し、沈降速度差によって粉粒体を微粒物と微粒物より粒径が大きい中粒物とに分級する。   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. That is, as shown to Fig.9 (a), a granular material processing system classifies a granular material into two or more groups while classifying into a coarse thing and a granular material, wash | cleaning a process target object. Further, as shown in FIG. 9B, the wet sorting means sorts the coarse product into a coarse product with a large specific gravity and a coarse product with a low specific gravity by the difference in specific gravity, and the fine particles and fine particles are separated by the difference in sedimentation speed. Classification into medium particles having a particle size larger than that of the particles.

粗大物搬出口125から排出された金属類、ガラ類は、磁選機等の金属回収部110によって金属とガラ類に分離して回収され、排水樋127に流出した溢流水は、水切りスクリーン128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手段400に送られる。この時、水切りスクリーン128部では、洗浄水を噴霧して有機質材を洗浄してもよい。   Metals and glass discharged from the bulk material outlet 125 are separated and collected by the metal recovery unit 110 such as a magnetic separator, and the overflow water flowing out to the drainage 127 is drained by a draining screen 128. After the organic material is removed, it is sent to the first re-cleaning means 400 together with the fine ash. At this time, the draining screen 128 may spray the cleaning water to clean the organic material.

脈動洗浄槽121の底部に形成した開口から洗浄水槽120の底部に沈降した中粒灰は、側部または底部に複数の小径の開口を形成したバケット129aが無限軌道に沿って複数並設されたバケットコンベア機構129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600によってさらに洗浄処理される。   A plurality of buckets 129a having a plurality of small-diameter openings formed side by side or at the bottom are arranged side by side along an endless track in the middle ash that has settled from the opening formed at the bottom of the pulsating washing tank 121 to the bottom of the washing water tank 120. While being drained by the bucket conveyor mechanism 129, it is carried out of the tank and further cleaned by the second re-cleaning means 600.

第一の再洗浄手段400は、水切りスクリーン128を経た溢流水が必要に応じて設けた中継槽140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142としてのシックナーに送られて濃縮される。尚、濃縮装置142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140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141を添加してもよい。   In the first re-cleaning means 400, the overflow water passing through the draining screen 128 is accumulated in the relay tank 140 provided as necessary, the concentration is uniformly stirred by the stirring pump, and the fine ash contained in the overflow water is discharged by the pump. It is sent to a thickener as the concentrating device 142 and concentrated. As the concentrating device 142, a known device such as a wet cyclone, a belt concentrator, or a centrifugal concentrator can be used. Further, a chemical agent 141 such as a flocculant such as a sulfuric acid band, a pH adjuster, or a chelating agent may be added to the relay tank 140.

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143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144で脱水洗浄されセメント原料に供される。尚、中継槽143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144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144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 143 and stirred and washed with new washing water supplied from the water supply tank 101, and then dehydrated and washed by the dehydration washing apparatus 144. To be served. In addition, without providing the relay tank 143, the fine ash concentrated by the thickener may be sent directly to the dehydrating and cleaning apparatus 144 and dehydrated while injecting cleaning water. As such a dehydration washing apparatus 144, 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142を設けず、微粒灰を中継槽140から直接脱水洗浄装置144へ送ってもよい。   Note that the fine ash may be sent directly from the relay tank 140 to the dehydration washing device 144 without providing the concentration device 142.

脱水洗浄装置144からの洗浄排水は中継槽145に排水され、最終的に貯留槽146に貯水される。   The washing waste water from the dehydrating and cleaning device 144 is drained into the relay tank 145 and finally stored in the storage tank 146.

貯留槽146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147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 146 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 147 and purified by the water treatment device and discharged outside the system. Is done.

濃縮装置142及び脱水洗浄装置144によって分離され貯留槽146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800を介して湿式選別手段200へ返送され、水噴射ノズル123a、123b、123c、123dを介して洗浄水槽120に再洗浄水として利用される。   The cleaning wastewater separated by the concentrating device 142 and the dehydrating and cleaning device 144 and stored in the storage tank 146 is returned to the wet sorting means 200 via the first circulation path 800 by the pump, and the water injection nozzles 123a, 123b, 123c, and 123d. It is used as re-washing water in the washing water tank 120 via

また、濃縮装置142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146を介さず貯留槽147へ送り、洗浄水が不足した場合のみ貯留槽146へ送り再洗浄水として利用する構成であってもよい。   Moreover, since the washing waste water separated by the concentrating device 142 has a high concentration of obstacle substances, it is preferentially discharged out of the system, so it is sent to the storage tank 147 without passing through the storage tank 146, and only when the washing water is insufficient. It may be configured to be sent to the storage tank 146 and used as rewash water.

尚、第一の循環経路800から供給される再洗浄水を、水噴射ノズル123a、123b、123c、123dを介して供給するルートとは別に、脈動洗浄槽121のプランジャ131の下部に設けた注水部121aから供給するルートを備え、各ルートを介した再洗浄水の供給比率を調整するように構成してもよい。注水部121aから供給する比率を調整し、脈動洗浄槽121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ができる。   In addition, the water injection provided in the lower part of the plunger 131 of the pulsation washing tank 121 separately from the route which supplies the rewash water supplied from the first circulation path 800 via the water injection nozzles 123a, 123b, 123c, and 123d. Routes supplied from the section 121a may be provided, and the supply ratio of rewash water through each route may be adjusted. By adjusting the ratio supplied from the water injection part 121a and adjusting the speed of the upward flow in the pulsation washing tank 121, the particle size to be classified can be set by controlling the sedimentation speed of the powder.

微粒灰の塩分含有量は、中流灰の塩分含有量よりも多く、第一の再洗浄手段400からの洗浄排水の塩分含有量は第二の再洗浄手段600の洗浄排水よりも高いため、第二の再洗浄手段600とは分離して湿式選別手段200へ返送するのである。   The salt content of the fine ash is higher than the salt content of the midstream ash, and the salt content of the cleaning effluent from the first re-cleaning means 400 is higher than the cleaning effluent of the second re-cleaning means 600. The second re-cleaning means 600 is separated and returned to the wet sorting means 200.

このようにして、湿式選別手段200及び第一の再洗浄手段400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142を経ることにより脱水洗浄装置144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 means 200 and the first re-cleaning means 400, the cleaning process is performed with the cleaning wastewater having a high salt concentration, but a new cleaning is supplied to the dehydration cleaning apparatus 144 via the concentration apparatus 142. The amount of water (rinse water) can be suppressed very slightly.

第二の再洗浄手段600は、バケットコンベア機構129によって槽外に搬出された中粒灰を粗粒灰と細粒灰に分級する分級装置161と、分級装置161で分級された細粒物を再洗浄する洗浄装置162を備えている。分級装置161は湿式の振動篩装置で構成され、バケットコンベア機構129からシュート160を介して落下供給される。尚、分級装置161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 600 classifies the medium ash carried out of the tank by the bucket conveyor mechanism 129 into coarse ash and fine ash, and the fine particles classified by the classification device 161. A cleaning device 162 for re-cleaning is provided. The classifying device 161 is configured by a wet vibrating screen device, and is dropped from the bucket conveyor mechanism 129 via the chute 160. A screen device can be used as the classification device 161.

シュート160及び分級装置161には、第二の循環経路900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161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 160 and the classifier 161 are sprayed with cleaning wastewater having a low salinity concentration circulated and supplied via the second circulation path 900, and new cleaning water is supplied from the water supply tank 101 on the downstream side of the classifier 161. 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162は、分級装置161を経た細粒物及び洗浄排水を貯留する中継槽163と、中継槽163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164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165を備えている。   The cleaning device 162 includes a relay tank 163 that stores fine particles and cleaning wastewater that have passed through the classification device 161, and a wet cyclone as a solid-liquid separator 164 that separates the fine ash that has been stirred and washed again in the relay tank 163 into a solid and liquid. And a washing tank 165 for washing the fine ash solid-liquid separated by the wet cyclone.

灰沈降槽で沈降した細粒灰は、灰掻揚げコンベア166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165の溢流水は中継槽163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 166, and then used as a cement material. . The overflow water in the cleaning tank 165 is circulated and supplied to the relay tank 163.

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160及び分級装置161に循環供給され、余剰の洗浄排水が貯留槽102に貯水された後に、湿式選別手段200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手段200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900を経て、再度、湿式選別手段200で分級される。尚、固液分離機164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 160 and the classifier 161 described above, and after the excess washing wastewater is stored in the storage tank 102, it is supplied as washing water for the wet sorting means 200. The The washing waste water separated by the wet cyclone contains fine ash that has not been sufficiently separated by the wet sorting means 200, and such fine ash passes through the second circulation path 900 and again by the wet sorting means 200. Classified. The solid-liquid separator 164 is not limited to a wet cyclone, and may be configured to separate fine ash and washing wastewater using a known dehydrator, a sedimentation tank, or the like.

第二の循環経路900は、洗浄槽165からの洗浄排水を中継槽163へ返送する循環経路191と、固液分離機164の排水を分級装置161へ返送する循環経路192を備えている。   The second circulation path 900 includes a circulation path 191 for returning the cleaning waste water from the cleaning tank 165 to the relay tank 163 and a circulation path 192 for returning the waste water of the solid-liquid separator 164 to the classifying device 161.

つまり、粉粒体の処理システムは、図9(c)に示すように、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手段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。   That is, as shown in FIG. 9 (c), the granular material processing system includes a first re-cleaning unit for re-cleaning the fine particles, a second re-cleaning unit for re-cleaning the medium particles, A first circulation path for returning cleaning wastewater discharged from one recleaning means to the wet sorting means; and a second circulation path for returning cleaning wastewater discharged from the second recleaning means to the second recleaning means. A circulation path is provided, and the washing wastewater returned through each circulation path is reused as washing water.

また、図9(d)に示すように、第一の再洗浄手段は、微粒物を濃縮する濃縮装置と、濃縮装置によって濃縮された微粒物を洗浄脱水する洗浄脱水装置を備え、濃縮装置によって分離された分離液を第一の循環経路を介して湿式選別手段へ返送する。   Further, as shown in FIG. 9 (d), the first re-cleaning means includes a concentrating device for concentrating the fine particles and a washing and dehydrating device for washing and dewatering the fine particles concentrated by the concentrating device. The separated separated liquid is returned to the wet sorting means through the first circulation path.

さらに、図10(a)に示すように、第二の再洗浄手段は、中粒物を粗粒物と細粒物に分級する分級装置と、分級された細粒物を再洗浄する洗浄装置を備えている。   Furthermore, as shown to Fig.10 (a), a 2nd re-washing means is a classifier which classifies a medium grain thing into a coarse grain thing and a fine grain thing, and a washing apparatus which re-washes the classified fine grain substance It has.

また、図10(b)に示すように、洗浄装置は、細粒物の中継槽と、再洗浄された細粒物を固液分離する固液分離機と、固液分離された細粒物を洗浄する洗浄槽とを備え、第二の循環経路は洗浄槽からの洗浄排水を中継槽へ返送する循環経路と、固液分離機の排水を前記分級装置へ返送する循環経路を備えている。   Further, as shown in FIG. 10 (b), the cleaning device includes a relay tank for fine particles, a solid-liquid separator for solid-liquid separation of the re-washed fine particles, and a fine-particle material that has been subjected to solid-liquid separation. The second circulation path has a circulation path for returning the washing waste water from the washing tank to the relay tank, and a circulation path for returning the waste water of the solid-liquid separator to the classification device. .

本実施形態では、中継槽163と固液分離機164が一段で構成される場合を示しているが、中継槽163と固液分離機を二段以上の複数段直列に配置するものであってもよく、その場合には、図11に示すように、第二の循環経路は後段の固液分離機の排水を前段の固液分離機の直前の中継槽へ移送する循環経路と、洗浄槽の排水を洗浄槽の直前の中継槽へ移送する循環経路と、一段目の固液分離機の排水を分級装置へ返送する循環経路を備えていることが好ましい。   In the present embodiment, the case where the relay tank 163 and the solid-liquid separator 164 are configured in one stage is shown, but the relay tank 163 and the solid-liquid separator are arranged in a plurality of stages in two or more stages. In this case, as shown in FIG. 11, the second circulation path includes a circulation path for transferring the waste water of the subsequent solid-liquid separator to the relay tank immediately before the solid-liquid separator, and a washing tank. It is preferable to provide a circulation path for transferring the waste water to the relay tank immediately before the washing tank and a circulation path for returning the waste water of the first-stage solid-liquid separator to the classification device.

以上説明したように、当該粉粒体の処理システムでは、粗大物が混入した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ために、湿式選別工程により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二以上の群に分級する粉粒体処理方法が実行され、湿式選別工程は、比重差によって粗大物を比重の大きい粗大物と比重の小さい粗大物に選別する比重選別工程と、沈降速度差によって粉粒体を微粒物と微粒物より粒径が大きい中粒物とに分級する分級工程が実行される。   As described above, in the processing system of the granular material, in order to clean the granular processing object mixed with coarse material and remove the obstacle substance mixed in the processing object, the processing object is processed by the wet sorting process. While the product is being washed, a coarse particle and a granular material are sorted and a granular material processing method is performed in which the granular material is classified into two or more groups, and the wet sorting process has a large specific gravity due to a difference in specific gravity. A specific gravity selection step of selecting a coarse product and a coarse product having a small specific gravity, and a classification step of classifying the granular material into a fine product and a medium product having a larger particle size than the fine product by a difference in settling speed are performed.

また、微粒物を再洗浄する第一の再洗浄工程と、中粒物を再洗浄する第二の再洗浄工程と、第一の再洗浄工程で排出された洗浄排水を湿式選別工程の洗浄水として返送するとともに、第二の再洗浄工程で排出された洗浄排水を第二の再洗浄工程の洗浄水として返送し、それぞれの洗浄排水を洗浄水として再利用される。   In addition, the first re-cleaning step for re-washing the fine particles, the second re-washing step for re-washing the medium-sized particles, and the washing wastewater discharged in the first re-washing step are used as washing water for the wet sorting step In addition, the cleaning wastewater discharged in the second rewashing process is returned as cleaning water in the second rewashing process, and each cleaning wastewater is reused as cleaning water.

そして、第二の再洗浄工程における再洗浄水の一部が湿式選別工程に戻されて、第一の再洗浄工程における再洗浄水として有効に利用される。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。   A part of the rewash water in the second rewash process is returned to the wet sorting process, and is effectively used as the rewash water in the first rewash process. 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.

上述したジグ選別装置18及び湿式選別手段200の洗浄槽がU字管形状に構成されるものを説明したが、洗浄槽の形状はU字管形状に限るものではなく、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。   Although the cleaning tank of the jig sorting device 18 and the wet sorting means 200 described above is configured in a U-shaped tube shape, the shape of the cleaning tank is not limited to the U-shaped tube shape, and the upper part branches into two. As long as the tube shape is connected to the lower portion, it may be V-shaped or Y-shaped.

以上説明した実施形態では、金属類、ガラ類、さらには有機質材といった粗大物が混入した焼却灰を処理対象物とする粉粒体処理システム及び粉粒体処理システムを説明したが、当該粉粒体処理システム及び粉粒体処理システムの処理対象物は焼却灰に限るものではなく、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、土砂から重金属類の汚染物質が洗浄除去される。   In the above-described embodiment, the powder processing system and the powder processing system have been described in which incinerated ash mixed with coarse materials such as metals, glass, and organic materials is treated. The object to be treated by the body treatment system and the particulate treatment system is not limited to incinerated ash, but is soil contaminated with heavy metals, such as landfilled soil illegally dumped. This method can also be applied to the case where the powdered soil particles are recycled as resources. In this case, heavy metal contaminants are washed away from the earth and sand.

上述の実施形態で説明した各部の具体的構成は例示に過ぎず、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。   The specific configuration of each part described in the above-described embodiment is merely an example, and it is needless to say that the design can be appropriately changed within the scope of the effects of the present invention.

本発明による焼却灰の処理設備を備えたゴミ焼却炉の説明図Explanatory drawing of the waste incinerator equipped with the incineration ash treatment facility according to the present invention 本発明による焼却灰の処理設備の洗浄装置の説明図Explanatory drawing of the washing | cleaning apparatus of the processing equipment of incineration ash by this invention 本発明による焼却灰の処理設備の説明図Explanatory drawing of incineration ash processing equipment according to the present invention 焼却主灰に含まれる塩素濃度の説明図Explanatory drawing of chlorine concentration in incineration main ash 本発明の別実施形態を示し、粉粒体の処理システムに用いられる湿式選別手段の説明図Explanatory drawing of the wet-sorting means which shows another embodiment of this invention and is used for the processing system of a granular material 同湿式選別手段の平面図Top view of the wet sorting means 同湿式選別手段の要部の説明図Explanatory drawing of the main part of the wet sorting means 粉粒体の処理システムの説明図Explanatory drawing of processing system of granular material 粉粒体の処理システムのブロック説明図Block explanatory diagram of powder processing system 粉粒体の処理システムのブロック説明図Block explanatory diagram of powder processing system 粉粒体の処理システムのブロック説明図Block explanatory diagram of powder processing system

符号の説明Explanation of symbols

1:ゴミピット
2A:バケット
2:クレーン装置
3:ホッパー
4:プッシャ
7:廃熱ボイラ
8:蒸気タービン
9:発電機
10:エコノマイザ
11:排ガス処理機構
12:誘引送風機
13:煙突
16:焼却処理帯
17:灰シュート
18:ジグ選別装置
19:洗浄水回収機構
20:洗浄槽
21:加振機構
22:浮遊物分離機構
23:不適物除去機構
24:第一分級装置
25:搬送機構
26:洗浄水補充機構
27:モータ
28:回転盤
29:ピストン
30:水振板
31:浮遊物排出口
32:浮遊物回収部
33:ポンプ
34:洗浄水管
35:メッシュコンベア機構
36a:金属回収機構
36b:破砕装置
37:バケット
38:バケットコンベア機構
39:第一散水装置
40:第二分級装置
41:第一再洗浄装置
42:灰沈降槽
43:掻き出し装置
44:第二再洗浄装置
45:第一脱水装置
46:スラリー化装置
47:第二脱水装置
48:脱水濾液槽
49:第一水処理装置
50:処理水槽
51:第二水処理装置
1: garbage pit 2A: bucket 2: crane device 3: hopper 4: pusher 7: waste heat boiler 8: steam turbine 9: generator 10: economizer 11: exhaust gas treatment mechanism 12: induction blower 13: chimney 16: incineration treatment zone 17 : Ash chute 18: Jig sorting device 19: Washing water recovery mechanism 20: Washing tank 21: Shaking mechanism 22: Floating substance separation mechanism 23: Improper object removal mechanism 24: First classifier 25: Transport mechanism 26: Washing water replenishment Mechanism 27: Motor 28: Turntable 29: Piston 30: Water vibrating plate 31: Floating material discharge port 32: Floating material collecting unit 33: Pump 34: Washing water pipe 35: Mesh conveyor mechanism 36a: Metal collecting mechanism 36b: Crushing device 37 : Bucket 38: Bucket conveyor mechanism 39: First sprinkler 40: Second classifier 41: First recleaning device 42: Ash settling tank 43: Scraping device 44 Second re-cleaning device 45: first dewatering device 46: slurrying device 47: the second dewatering device 48: dehydration filtrate tank 49: first water treatment apparatus 50: treatment water tank 51: second water treatment apparatus

Claims (13)

焼却灰を洗浄処理する焼却灰の処理方法であって、
焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する第一工程と、前記第一工程で分離洗浄された焼却主灰を分級する第二工程を備える焼却灰の処理方法。
An incineration ash treatment method for cleaning incineration ash,
Incineration ash comprising a first step of cleaning the incinerated main ash separated and recovered from the incinerated ash while separating unburned and unsuitable materials, and a second step of classifying the incinerated main ash separated and washed in the first step Processing method.
前記焼却灰から分離回収された焼却主灰が、事前に洗浄されることなく、前記第一工程に投入される請求項1記載の焼却灰の処理方法。   The incineration ash treatment method according to claim 1, wherein the incineration main ash separated and recovered from the incineration ash is put into the first step without being washed in advance. 前記第一工程は、洗浄水が充填された洗浄槽に焼却主灰を投入して、洗浄水に浮遊する未燃物を分離する浮遊物分離工程と、洗浄水に沈降する不適物を除去する不適物除去工程と、浮遊物及び不適物が除去された焼却主灰を後段の分級工程に搬送する搬送工程とを備えている請求項1または2記載の焼却灰の処理方法。   In the first step, the incinerated main ash is put into a washing tank filled with washing water to remove unburned substances floating in the washing water, and unsuitable items that settle in the washing water are removed. The incinerated ash treatment method according to claim 1, further comprising: an unsuitable substance removing step; and a transporting step of transporting the incinerated main ash from which suspended matter and unsuitable materials have been removed to a subsequent classification step. 前記第一工程は、充填された洗浄水が上下に脈動する脈動洗浄槽に投入された焼却主灰を洗浄しながら、比重差によって焼却主灰に含まれる未燃物を浮遊させて上層の洗浄水とともに搬出する浮遊物分離工程と、比重差によって洗浄水に沈降する不適物を受け止めて搬出する不適物除去工程と、底部に沈降する焼却主灰を後段の分級工程に搬送する搬送工程を備えている請求項1または2記載の焼却灰の処理方法。   In the first step, while washing the incinerated main ash charged into the pulsation washing tank in which the filled washing water pulsates up and down, the unburned matter contained in the incinerated main ash is floated by the specific gravity difference, and the upper layer is washed Equipped with a floating substance separation process that carries out with water, an unsuitable substance removal process that accepts and discharges unsuitable substances that settle in the washing water due to the difference in specific gravity, and a transportation process that transports the incinerated main ash that settles to the bottom to the subsequent classification process The incineration ash processing method according to claim 1 or 2. 焼却灰を洗浄処理する焼却灰の処理方法であって、
焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する洗浄工程と、洗浄工程後の焼却主灰を予め複数段に設定された基準粒径に基づいて分級する分級工程と、分級工程後の小径側の焼却主灰を再洗浄する再洗浄工程とを備え、洗浄工程後の焼却主灰に対して前記基準粒径が大から小なる順に前記分級工程と前記再洗浄工程を繰り返す焼却灰の処理方法。
An incineration ash treatment method for cleaning incineration ash,
The incineration main ash separated and recovered from the incineration ash is cleaned while separating unburned and unsuitable materials, and the incineration main ash after the cleaning process is classified based on a standard particle size set in multiple stages in advance. A classification step, and a re-washing step for re-washing the incineration main ash on the small diameter side after the classification step, the classification step and the above in order from the largest to the smallest particle size with respect to the incineration main ash after the washing step Incineration ash treatment method that repeats the re-cleaning process.
前記洗浄工程は、洗浄水が充填された洗浄槽に焼却主灰を投入して、浮遊する未燃物を分離する浮遊物分離工程と、沈降する不適物を除去する不適物除去工程と、浮遊物及び不適物が除去された焼却主灰を後段の分級工程に搬送する搬送工程と、前記洗浄槽に洗浄水を補充する洗浄水補充工程を備えている請求項5記載の焼却灰の処理方法。   The cleaning step includes injecting the main incinerator ash into a cleaning tank filled with cleaning water to separate the floating unburned matter, the unsuitable matter removing step for removing the unsuitable matter that settles, and the floating step. 6. A method for treating incinerated ash according to claim 5, further comprising: a transporting step for transporting the incinerated main ash from which the waste and unsuitables have been removed to a subsequent classification step; . 前記不適物除去工程で除去された不適物に対して金属を除去した後に破砕処理し、被破砕処理物を前記洗浄工程に投入する請求項6記載の焼却灰の処理方法。   The method for treating incinerated ash according to claim 6, wherein metal is removed from the unsuitable material removed in the unsuitable material removing step and then crushed, and the material to be crushed is put into the washing step. 焼却灰を洗浄処理する焼却灰の処理設備であって、
焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する洗浄装置と、洗浄後の焼却主灰を分級する分級装置とを備えて構成される焼却灰の処理設備。
Incineration ash processing equipment for cleaning incineration ash,
Incineration ash processing equipment comprising a cleaning device that cleans incinerated main ash separated and recovered from incinerated ash while separating unburned and unsuitable materials, and a classification device that classifies the incinerated main ash after cleaning .
前記洗浄装置が、洗浄水が充填され、上部が二つに分岐し下部が連結された管形状の脈動洗浄槽と、前記脈動洗浄槽内の洗浄水を脈動させる脈動発生装置と、前記脈動洗浄槽に投入された焼却主灰を洗浄しながら、比重差によって焼却主灰に含まれる未燃物を浮遊させて上層の洗浄水とともに搬出する排出口と、比重差によって洗浄水に沈降する不適物を受け止めて搬出するコンベア装置と、底部に沈降する焼却主灰を後段の分級工程に搬送するコンベア装置を備えている請求項8記載の焼却灰の処理設備。   The cleaning device is filled with cleaning water, has a tubular pulsation cleaning tank in which the upper part is branched into two and the lower part is connected, a pulsation generator for pulsating the cleaning water in the pulsating cleaning tank, and the pulsating cleaning While washing the incinerator main ash that has been put into the tank, the unburned material contained in the incinerator main ash is floated due to the difference in specific gravity, and discharged with the upper cleaning water. The incineration ash processing equipment according to claim 8, further comprising: a conveyor device that receives and conveys the incinerator main ash that sinks to the bottom and conveys the incinerated main ash to a subsequent classification step. 焼却灰を洗浄処理する焼却灰の処理設備であって、
焼却灰から分離回収された焼却主灰を未燃物や不適物を分離しながら洗浄する洗浄装置と、洗浄後の焼却主灰を予め複数段に設定された基準粒径に基づいて大から小なる順に分級する複数の分級装置と、各分級装置の後段に設置され、小径側に分級された焼却主灰を再洗浄する複数の再洗浄装置と、前記再洗浄装置で再洗浄された焼却主灰を脱水処理する脱水装置を備えて構成される焼却灰の処理設備。
Incineration ash processing equipment for cleaning incineration ash,
A cleaning device that cleans the incinerated main ash separated and recovered from the incinerated ash while separating unburned and unsuitable materials, and the main size of the incinerated main ash after cleaning based on standard particle sizes set in multiple stages. A plurality of classifiers for classifying in that order, a plurality of rewashing devices installed at the subsequent stage of each classifying device to rewash the incinerated main ash classified on the small diameter side, and the incinerators rewashed by the recleaning device Incineration ash treatment equipment that is equipped with a dehydration device that dehydrates ash.
前記洗浄装置は、洗浄水が充填された洗浄槽と、前記洗浄槽に充填された洗浄水を脈動させる加振機構と、前記洗浄槽に投入された焼却主灰から浮遊する未燃物を分離する浮遊物分離機構と、沈降する不適物を除去する不適物除去機構と、浮遊物及び不適物が除去され、底部に沈殿した焼却主灰を後段の分級装置に搬送する搬送機構と、洗浄水を前記洗浄槽に補充する洗浄水補充機構を備えたジグ選別装置で構成されている請求項8から10の何れかに記載の焼却灰の処理設備。   The cleaning device separates a floating tank filled with cleaning water, a vibration mechanism that pulsates the cleaning water filled in the cleaning tank, and unburned substances floating from the incinerated main ash charged into the cleaning tank. Floating substance separation mechanism, unsuitable substance removal mechanism that removes unsuitable sediments, a transport mechanism that removes suspended matter and unsuitable substances and settles the incinerated main ash that has settled to the bottom, to a subsequent classifier, and washing water The incineration ash treatment facility according to any one of claims 8 to 10, comprising a jig sorting device having a washing water replenishing mechanism for replenishing the washing tank. 前記洗浄装置に形成された焼却主灰の投入部が焼却炉の灰シュート下部に設けられ、炉内で焼却処理され前記灰シュートから落下した焼却主灰が投入される請求項8から11の何れかに記載の焼却灰の処理設備。   The incinerator main ash input portion formed in the cleaning device is provided below the ash chute of the incinerator, and the incinerated main ash that has been incinerated in the furnace and dropped from the ash chute is input. Incineration ash processing equipment described in Crab. 粗大物が混入した粉粒状の処理対象物を洗浄処理する処理設備であって、
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洗浄装置と、前記洗浄装置で分離洗浄された粉粒体を分級する分級装置とを備えて構成される処理設備。
A processing facility for cleaning a granular processing object mixed with a coarse material,
A processing facility comprising a cleaning device that sorts a coarse object and a granular material while cleaning an object to be processed, and a classification device that classifies the granular material separated and washed by the cleaning device.
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