[go: up one dir, main page]
More Web Proxy on the site http://driver.im/

JP4943309B2 - Powder processing system and powder processing method - Google Patents

Powder processing system and powder processing method Download PDF

Info

Publication number
JP4943309B2
JP4943309B2 JP2007319104A JP2007319104A JP4943309B2 JP 4943309 B2 JP4943309 B2 JP 4943309B2 JP 2007319104 A JP2007319104 A JP 2007319104A JP 2007319104 A JP2007319104 A JP 2007319104A JP 4943309 B2 JP4943309 B2 JP 4943309B2
Authority
JP
Japan
Prior art keywords
cleaning
washing
fine particles
coarse
circulation path
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
JP2007319104A
Other languages
Japanese (ja)
Other versions
JP2009136846A (en
Inventor
耕大 吉崎
雄一 米津
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kubota Corp
Original Assignee
Kubota Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kubota Corp filed Critical Kubota Corp
Priority to JP2007319104A priority Critical patent/JP4943309B2/en
Publication of JP2009136846A publication Critical patent/JP2009136846A/en
Application granted granted Critical
Publication of JP4943309B2 publication Critical patent/JP4943309B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/52Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/60Glass recycling
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)

Description

本発明は、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除去する粉粒体処理システム及び粉粒体処理方法に関する。   The present invention relates to a granular material processing system and a granular material processing method for cleaning a granular processing object mixed with a coarse material and removing an obstacle substance 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1に記載されたような比重選別方法では、焼却灰に混入された灰よりも比重の小さな雑多な浮遊物を分離除去することができないという問題があり、また、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, the specific gravity sorting method as described in Patent Document 1 has a problem that it is not possible to separate and remove various suspended matters having a specific gravity smaller than the ash mixed in the incinerated ash. As described, incinerated ash and soil with various particle size distributions, the contamination concentration of obstacles such as salts and heavy metals varies depending on the particle size, so it is extremely difficult to wash uniformly in the same aquarium. It is.

一方、特許文献2に記載された洗浄処理方法では、事前に焼却灰から粗大物を分離除去する必要があり、上述した従来の問題点が解消されるものではない。   On the other hand, in the cleaning method described in Patent Document 2, it is necessary to separate and remove coarse materials from the incinerated ash in advance, and the conventional problems described above are not solved.

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、処理対象物に混在する粗大物を分離除去して粉粒体から塩素等の障害物質を効率的に除去することができる粉粒体処理システム及び粉粒体処理方法を提供することを目的とする。 In view of the above-mentioned problems, the present invention simplifies equipment and reduces the amount of washing water, while separating and removing coarse substances mixed in the object to be processed, and efficiently removing obstacle substances such as chlorine from the granular material. An object of the present invention is to provide a granular material processing system and a granular material processing method that can be used.

上述の目的を達成するため、本発明による粉粒体処理システム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、粗大物が混入した粉粒状の焼却灰を洗浄して該焼却灰に混入し、資源として再利用する際に障害となる塩素を除去する粉粒体処理システムであって、前記粗大物が混入した焼却灰を洗浄しながら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焼却灰を塩素含有量が相対的に多い微粒物と、微粒物より粒径が大きい塩素含有量が相対的に少ない中粒物とを含む二以上の群に分級する湿式選別手段と、前記微粒物を再洗浄する第一の再洗浄手段と、前記中粒物を再洗浄する第二の再洗浄手段と、前記第一の再洗浄手段から排出された塩素含有量が相対的に多い洗浄排水を前記湿式選別手段へ返送する第一の循環経路と、前記第二の再洗浄手段から排出された塩素含有量が相対的に少ない洗浄排水を前記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点にある。 In order to achieve the above-mentioned object, the first characteristic configuration of the granular material processing system according to the present invention is that, as described in claim 1 of the claims, the granular incineration ash mixed with coarse substances is used. A granular processing system that removes chlorine that becomes a hindrance when reused as a resource after being washed and mixed into the incinerated ash, and is a coarse product due to a difference in specific gravity while washing the incinerated ash mixed with the coarse product Are classified into coarse products with a large specific gravity and coarse products with a low specific gravity, and the incineration ash has a relatively large chlorine content and a relatively small chlorine content larger than the fine particles due to the difference in sedimentation speed. Wet sorting means for classifying into two or more groups containing medium granules, first rewash means for re-washing the fine granules, second re-washing means for re-washing the medium granules, Relatively high chlorine content discharged from the first re-cleaning means A first circulation path for returning purified wastewater to the wet sorting means, and a first circulation path for returning cleaning wastewater having a relatively low chlorine content discharged from the second rewashing means to the second rewashing means. There are two circulation paths, and the cleaning wastewater returned through each circulation path is reused as cleaning water .

湿式選別手段により、処理対象物が洗浄されながら粗大物と粉粒体である焼却灰とに選別されるとともに、焼却灰が二以上の群に分級されるようになり、選別装置と分級装置を各別に設ける必要が無く、設備費の低減を図るとともに洗浄水量を低減しながらも、効率的に選別洗浄を行なうことができるようになる。 The wet sorting means sorts the processing target object into coarse and granular incineration ash while being cleaned, and the incineration ash is classified into two or more groups. separately to need not be provided, while reducing the amount of wash water with reduced equipment cost, ing to be able to efficiently perform screening washing.

湿式選別手段により分級された障害物質である塩素含有量の多い微粒物が第一の再洗浄手段により再洗浄され、微粒物よりも障害物質である塩素含有量が少ない中粒物が第二の再洗浄手段により再洗浄される。このとき、第一の再洗浄手段から排出された塩素濃度が高い洗浄排水が第一の循環経路を介して湿式選別手段へ返送されて洗浄水として再利用され、第二の再洗浄手段から排出された塩素濃度が比較的低い洗浄排水が第二の循環経路を介して第二の再洗浄手段へ返送されて洗浄水として再利用される。従って、第一の循環経路では塩素濃度の高い微粒物が洗浄される結果、相対的に洗浄排水の塩素濃度が高くなるが、第二の循環経路では塩素濃度が比較的低い洗浄排水で障害物質の含有量が少ない中粒物が洗浄されるようになり、洗浄水量を低減しながらも、洗浄排水を効率的に再利用し洗浄効果を高めることが可能となる。 Many fines of a humidity-based separation means is classified faults substance chlorine content is re-cleaned by the first re-cleaning means, the grain was the second in a small chlorine content is a disorder substance than fines It is re-cleaned by the re-cleaning means. At this time, cleaning wastewater with high chlorine concentration discharged from the first recleaning means is returned to the wet sorting means via the first circulation path and reused as cleaning water, and discharged from the second recleaning means. are chlorine concentration is relatively low washing wastewater Ru is reused as a second wash water is returned via the circulating path to the second re-cleaning means. Therefore, as a result of washing fine particles with a high chlorine concentration in the first circulation path, the chlorine concentration in the washing wastewater is relatively high, but in the second circulation path, the obstacle substance is contained in the washing wastewater with a relatively low chlorine concentration. It becomes possible to wash the medium-grained material with a low content of slag and to efficiently reuse the washing wastewater and enhance the washing effect while reducing the amount of washing water .

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、前記第一の再洗浄手段は、前記微粒物を濃縮する濃縮装置と、前記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、前記濃縮装置によって分離された分離液を前記第一の循環経路を介して前記湿式選別手段へ返送する点にある。 In the second characteristic configuration, as described in claim 2, in addition to the first characteristic configuration described above, the first re-cleaning means includes a concentrating device for concentrating the fine particles, and the concentrating device. A cleaning and dehydrating device for cleaning and dewatering the concentrated fine particles is provided, and the separated liquid separated by the concentrating device is returned to the wet sorting means through the first circulation path.

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三特徴構成に加えて、前記第二の再洗浄手段は、前記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点にある。 In the third feature configuration, as described in claim 3, in addition to the first or third feature configuration described above, the second re-cleaning means is configured to change the medium-sized product into a coarse product and a fine product. It is in the point provided with the classifier which classifies into a thing, and the washing | cleaning apparatus which rewashs the classified fine particle thing.

分級装置で分級された細粒物は、粗粒物に比べて障害物質の含有量が多いため、洗浄装置により再洗浄されることにより十分に浄化される。   The fine particles classified by the classifier have a higher content of obstructive substances than the coarse particles, and thus are sufficiently purified by being washed again by the cleaning device.

同第四の特徴構成は、同請求項4に記載した通り、上述の第三特徴構成に加えて、前記洗浄装置は、前記細粒物の中継槽と、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、前記第二の循環経路は前記洗浄槽からの洗浄排水を前記中継槽へ返送する循環経路と、前記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点にある。 In the fourth feature configuration, as described in claim 4, in addition to the third feature configuration described above, the cleaning device fixes the relay tank for the fine granules and the re-washed fine granules. A solid-liquid separator for liquid separation; and a washing tank for washing fine particles separated into solid and liquid, wherein the second circulation path is a circulation path for returning washing waste water from the washing tank to the relay tank; The solid-liquid separator is provided with a circulation path for returning the waste water from the solid-liquid separator to the classification device.

同第五の特徴構成は、同請求項5に記載した通り、上述の第四特徴構成に加えて、前記中継槽と前記固液分離機が複数段直列に配置され、前記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、前記洗浄槽の排水を前記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前記分級装置へ返送する循環経路を備えている点にある。 In the fifth feature configuration, as described in claim 5, in addition to the fourth feature configuration described above, the relay tank and the solid-liquid separator are arranged in a plurality of stages in series, and the second circulation path Is a circulation path for transferring the waste water of the latter solid-liquid separator to the relay tank immediately before the preceding solid-liquid separator, a circulation path for transferring the waste water of the washing tank to the relay tank immediately before the washing tank, The circulation path for returning the waste water of the eye solid-liquid separator to the classifier is provided.

本発明による粉粒体処理方法の第一の特徴構成は、同請求項に記載した通り、粗大物が混入した粉粒状の焼却灰を洗浄して該焼却灰に混入し、資源として再利用する際に障害となる塩素を除去する粉粒体処理方法であって、前記粗大物が混入した焼却灰を洗浄しながら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焼却灰を塩素含有量が相対的に多い微粒物と、微粒物より粒径が大きい塩素含有量が相対的に少ない中粒物とを含む二以上の群に分級する分級工程とを含む湿式選別工程と、前記微粒物を再洗浄する第一の再洗浄工程と、前記中粒物を再洗浄する第二の再洗浄工程と、前記第一の再洗浄工程から排出された塩素含有量が相対的に多い洗浄排水を前記湿式選別工程へ返送する第一の循環工程と、前記第二の再洗浄工程から排出された塩素含有量が相対的に少ない洗浄排水を前記第二の再洗浄工程へ返送する第二の循環工程を備え、それぞれの循環工程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点にある。 The first characteristic configuration of the granular material processing method according to the present invention is that, as described in claim 6 , the granular incineration ash mixed with a coarse product is washed and mixed into the incineration ash and reused as a resource. This is a powder and particle processing method that removes chlorine that becomes an obstacle in the process , and the coarse product is sorted into a coarse product with a large specific gravity and a coarse product with a low specific gravity by washing the incinerated ash mixed with the coarse product by the specific gravity difference. Two or more groups including a specific gravity sorting step, fine particles having a relatively high chlorine content in the incinerated ash due to a difference in sedimentation speed, and medium particles having a relatively small chlorine content and a larger particle size than the fine particles. A wet sorting step including a classification step, a first re-washing step for re-washing the fine particles, a second re-washing step for re-washing the medium particles, and the first re-washing Washing wastewater with relatively high chlorine content discharged from the process A first circulation step for returning to the second step, and a second circulation step for returning the washing waste water with a relatively low chlorine content discharged from the second rewashing step to the second rewashing step. The cleaning wastewater returned through each circulation process is reused as cleaning water .

同第二の特徴構成は、同請求項に記載した通り、上述の第一特徴構成に加えて、前記第一の再洗浄工程は、前記微粒物を濃縮する濃縮工程と、前記濃縮工程によって濃縮された微粒物を洗浄脱水する洗浄脱水工程を備え、前記濃縮工程によって分離された分離液を前記第一の循環工程により前記湿式選別工程へ返送する点にある。 In the second feature configuration, as described in claim 7 , in addition to the first feature configuration described above, the first re-washing step includes a concentration step for concentrating the fine particles, and a concentration step. There is a washing and dehydration step for washing and dewatering the concentrated fine particles, and the separated liquid separated by the concentration step is returned to the wet sorting step by the first circulation step .

同第三の特徴構成は、同請求項に記載した通り、上述の第一または第二特徴構成に加えて、前記第二の再洗浄工程は、前記中粒物を粗粒物と細粒物に分級する分級工程と、分級された細粒物を再洗浄する洗浄工程を備えている点にある。 In the third feature configuration, as described in claim 8 , in addition to the first or second feature configuration described above, the second re-cleaning step may be configured such that the medium-sized product is a coarse product and a fine product. It is in the point provided with the classification process which classifies into a thing, and the washing process which re-washes the classified fine particle thing .

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、処理対象物に混在する粗大物を分離除去して粉粒体から塩素等の障害物質を効率的に除去することができる粉粒体処理システム及び粉粒体処理方法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, coarse substances mixed in the object to be treated are separated and removed to efficiently remove obstacle substances such as chlorine from the granular material. It has become possible to provide a granular material processing system and a granular material processing method that can be removed.

以下に、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除去する粉粒体処理システム及び粉粒体処理方法を、図面に基づいて説明する。ここでは、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焼却灰を処理対象物とする場合を説明する。   Hereinafter, a granular material processing system and a granular material processing method for cleaning a granular processing object mixed with a coarse material and removing an obstacle substance mixed in the processing object will be described with reference to the drawings. Here, a case will be described in which incineration ash mixed with coarse materials such as metals, glass (stones, glass pieces, etc.) and organic materials (rubber, plastic, paper, fiber, wood pieces, etc.) is used as the object to be treated.

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く、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。   The incinerated ash has a different chlorine content depending on the particle size, and the smaller the particle size, the larger the chlorine content. In the present granular material processing system, coarse particles having a particle size of 2 mm or more based on the chlorine content (hereinafter, “ ), Fine particles having a particle size of 0.15 mm to 2 mm (hereinafter also referred to as “fine ash”), and fine particles having a diameter smaller than 0.15 mm (hereinafter, “fine ash”). Dechlorination treatment is performed efficiently by changing the cleaning conditions in each of the above.

図4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に分級する湿式選別手段2と、湿式選別手段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、湿式選別手段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. 4, 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. Wet-sorting means 2 for classifying into two, first re-washing means 4 for re-washing the fine particles classified by the wet-sorting means 2, and second-washing for the medium-grained substances classified by the wet sorting means 2 A re-cleaning means 6 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手段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 first waste water discharged from the first re-cleaning means 4 is returned to the wet sorting means 2 and the waste water 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、湿式選別手段2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20と、一方の上部開口が洗浄水槽20と連通し、他方の開口に脈動発生装置30が設けられたU字管形状の脈動洗浄槽21と、脈動洗浄槽21の一方の開口及び洗浄水槽20の傾斜底部に沿って配置され、プーリー22a,22b,22c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22と、コンベアベルト22の回転方向に沿って複数設けられ、コンベアベルト22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23a、23b、23c、23dを備えたジグ選別装置で構成されている。   As shown in FIG. 1 to FIG. 3, the wet sorting means 2 includes a washing water tank 20 having a rectangular shape in plan view that is filled with washing water and has an inclined bottom part, and one upper opening communicates with the washing water tank 20, and the other opening A U-shaped pulsating washing tank 21 provided with a pulsation generating device 30 and one opening of the pulsating washing tank 21 and an inclined bottom part of the washing water tank 20 are arranged and rotated and supported by pulleys 22a, 22b and 22c. A plurality of conveyor belts 22 having a mesh-like transport surface, and water jet nozzles 23a and 23b which are provided in plural along the rotation direction of the conveyor belt 22 and form a water flow in a direction opposite to the rotation direction of the conveyor belt 22. , 23c, and 23d.

脈動発生装置30は、脈動洗浄槽21の他方の開口の水面近傍からベローズ37、ロッド32を介してプランジャ31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33を備え、エキセントリックシーブ33の回転軸を回転駆動するモータ34を備えている。   The pulsation generator 30 includes an eccentric sheave 33 connected to move the plunger 31 up and down from the vicinity of the water surface of the other opening of the pulsation washing tank 21 via a bellows 37 and a rod 32, and the rotational shaft of the eccentric sheave 33 is provided. A motor 34 that rotates is provided.

インバータ装置によりモータ34の回転数が調整され、モータ34の回転に伴なってベローズ37が伸縮作動されることにより、脈動洗浄槽21を介して洗浄水槽20内の水が上下方向に脈動する。   The rotation speed of the motor 34 is adjusted by the inverter device, and the bellows 37 is expanded and contracted with the rotation of the motor 34, whereby the water in the cleaning water tank 20 pulsates in the vertical direction via the pulsating cleaning tank 21.

脈動発生装置30は、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、脈動する液面の高さを変更することができる。   The pulsation generator 30 includes a stroke length adjustment mechanism (not shown) that adjusts the stroke length of the plunger 31 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、ロッド32のエキセントリックシーブ33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 attachment position of the plunger 31 in the vertical direction, a mechanism for adjusting the length of the rod 32, and a mechanism for adjusting the position of the rod 32 attached to the eccentric sheave 33 in the diametrical direction are used. Can do.

脈動洗浄槽21は、コンベアベルト22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35が取付けられたエキセントリックシーブ33が配され、位相が異なる脈動が付与される。   The pulsation washing tank 21 is divided into three along the extending direction of the conveyor belt 22, and eccentric sheaves 33 to which the rotating shafts 35 are attached at different eccentric positions are arranged, and pulsations with different phases are applied.

ベルトコンベア装置36によって湿式選別手段2に搬送された処理対象物は、振動フィーダ24により洗浄水槽20に投入され、脈動洗浄槽21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22によって粗大物搬出口25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23a、23b、23c、23dによる水流に従って溢流堰26から排水樋27に流出する。即ち、湿式選別手段2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。   The processing object conveyed to the wet sorting means 2 by the belt conveyor device 36 is put into the washing water tank 20 by the vibration feeder 24, dispersed by the vertical pulsation of the washing water by the pulsation washing tank 21, 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 25 by the conveyor belt 22 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 26 to the drainage basin 27 according to the water flow by the water injection nozzles 23a, 23b, 23c, 23d. That is, in the wet sorting means 2, a specific gravity sorting step is performed in which the coarse product is sorted into a coarse product having a large specific gravity and a coarse product having a low specific gravity by the specific gravity difference.

また、洗浄水槽20に投入された灰は、脈動洗浄槽21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。即ち、湿式選別手段2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。   The ash charged into the washing water tank 20 is dispersed by the pulsation in the vertical direction of the washing water in the pulsating washing tank 21, and the medium ash (coarse ash having a large sedimentation speed and settled against the upward pulsating flow. And fine ash) settle in the water tank, and the fine ash having a low settling velocity floats in the washing water according to the water flow by the water injection nozzles 23a, 23b, 23c, and 23d and flows out from the overflow weir 26 to the drainage basin 27. That is, in the wet sorting means 2, 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 diameter 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5(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5(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.5 (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. In addition, as shown in FIG. 5B, 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 specific gravity difference, and the fine particles and fine particles are separated by the sedimentation speed difference. Classification into medium particles having a particle size larger than that of the particles.

粗大物搬出口25から排出された金属類、ガラ類は、磁選機等の金属回収部10によって金属とガラ類に分離して回収され、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手段4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。   Metals and glass discharged from the bulky material outlet 25 are separated and recovered by the metal recovery unit 10 such as a magnetic separator, and the overflow water flowing into the drainage basin 27 is discharged by the draining screen 28. After the organic material is removed, it is sent to the first re-cleaning means 4 together with the fine ash. At this time, the organic material may be washed by spraying washing water on the draining screen 28 part.

脈動洗浄槽21の底部に形成した開口から洗浄水槽20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29a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によってさらに洗浄処理される。   A plurality of buckets 29a 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 21 to the bottom of the washing water tank 20. 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.

第一の再洗浄手段4は、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。   In the first re-cleaning means 4, the overflow water that has passed through the draining screen 28 is accumulated in a relay tank 40 provided as necessary, the concentration is uniformly stirred by a stirring pump, and the fine ash contained in the overflow water is It is sent to a thickener as the concentrating device 42 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を介して湿式選別手段2へ返送され、水噴射ノズル23a、23b、23c、23dを介して洗浄水槽20に再洗浄水として利用される。   The washing waste water separated by the concentrating device 42 and the dehydrating washing device 44 and stored in the storage tank 46 is returned to the wet sorting means 2 through the first circulation path 8 by the pump, and the water injection nozzles 23a, 23b, 23c, 23d. Is used as re-cleaning water in the cleaning water tank 20.

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.

尚、第一の循環経路8から供給される再洗浄水を、水噴射ノズル23a、23b、23c、23dを介して供給するルートとは別に、脈動洗浄槽21のプランジャ31の下部に設けた注水部21a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21aから供給する比率を調整し、脈動洗浄槽21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 31 of the pulsation washing tank 21 separately from the route which supplies the rewash water supplied from the 1st circulation path 8 via the water injection nozzles 23a, 23b, 23c, and 23d. Routes supplied from the unit 21a 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 section 21a and adjusting the speed of the upward flow in the pulsation washing tank 21, 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、湿式選別手段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 means 2 and the first re-cleaning means 4, the cleaning treatment is performed with the cleaning wastewater having a high salt concentration, but the new cleaning 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灰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 medium ash 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、湿式選別手段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手段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、湿式選別手段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 to the chute 60 and the classifier 61 as washing water, and after the excess washing wastewater is stored in the storage tank 100, it is supplied as washing water for the wet sorting means 2. The The washing waste water separated by the wet cyclone contains fine ash that has not been sufficiently separated by the wet sorting means 2, and such fine ash passes through the second circulation path 9 and again by the wet sorting means 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、図5(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, the granular material processing system according to the present invention includes, as shown in FIG. 5C, a first re-cleaning unit that re-cleans the fine particles, and a second re-cleaning unit that re-cleans the medium particles. A first circulation path for returning cleaning wastewater discharged from the first recleaning means to the wet sorting means; and a first circulation path for returning cleaning wastewater discharged from the second recleaning means to the second recleaning means. Two circulation paths are provided, and the washing wastewater returned through each circulation path is reused as washing water.

また、図5(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. 5 (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6(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.6 (a), a 2nd re-washing means is a classifier which classify | categorizes a medium grain thing into a coarse grain thing and a fine grain thing, and a washing apparatus which rewashs the classified fine grain substance It has.

また、図6(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。   Moreover, as shown in FIG.6 (b), the washing | cleaning apparatus is a relay tank of a fine particle thing, the solid-liquid separator which carries out solid-liquid separation of the re-washed fine particle, and the fine particle by which solid-liquid separation was carried out 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63と固液分離機64が一段で構成される場合を示しているが、中継槽63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7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 63 and the solid-liquid separator 64 are configured in one stage is shown, but the relay tank 63 and the solid-liquid separator are arranged in a plurality of stages in two or more stages. In this case, as shown in FIG. 7, 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 classifier.

以上説明したように、本発明による粉粒体処理システムでは、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 granular material processing system according to the present invention, in order to clean the granular processing object mixed with the coarse material and remove the obstacle substance mixed in the processing object, the wet particle sorting process is performed. While washing the target object, 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. A specific gravity selection step for selecting a large coarse product and a coarse product with a low specific gravity, and a classification step for classifying the granular material into fine particles and medium particles having a larger particle diameter than the fine particles by the difference in settling speed are executed.

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、粉粒体から塩素等の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, the coarse substances mixed in the object to be treated are washed and removed, and the circulation route of the washing wastewater is separated into two systems, so that chlorine and the like can be separated from the granular material. It becomes possible to efficiently remove obstacle substances such as water-soluble components and heavy metals .

上述した実施形態では、湿式選別手段がジグ選別装置で構成されるものを説明したが、このような湿式選別手段に限るものではなく、図8及び図9に示すような湿式選別手段であってもよい。 In the above-described embodiment, the wet sorting unit is configured by the jig sorting unit. However, the wet sorting unit is not limited to such a wet sorting unit, and is a wet sorting unit as shown in FIGS. 8 and 9. Also good.

詳述すると、湿式選別手段は、傾斜壁面71に沿ってメッシュコンベア72が配置された洗浄水槽7を、メッシュコンベア72の下端部から垂直方向に延出するように配置されたバースクリーン73によって紙面右方の選別槽7aと、紙面左方の分級槽7bに領域分離されている。   More specifically, the wet-sorting means uses a bar screen 73 arranged to extend the washing water tank 7 in which the mesh conveyor 72 is arranged along the inclined wall surface 71 from the lower end of the mesh conveyor 72 in the vertical direction. The region is divided into a sorting tank 7a on the right side and a classification tank 7b on the left side of the drawing.

選別槽7aではメッシュコンベア72側の上方から投入される処理対象物のうち比重の大きな粗大物をメッシュコンベア72で槽外に選別排出するとともに、バースクリーン73で捕捉された比重の小さな粗大物を槽外に掻上げ排出する掻上げレーキ76が無限軌道に沿って配置された掻上げ装置75により槽外に選別排出する。   The sorting tank 7a sorts and discharges a coarse article having a large specific gravity out of the tank to be processed from the upper side of the mesh conveyor 72 by the mesh conveyor 72, and a coarse article having a small specific gravity captured by the bar screen 73. A scraping rake 76 that lifts and discharges outside the tank is sorted and discharged out of the tank by a scraping device 75 arranged along an endless track.

掻上げレーキ76は、スプロケット75aに巻回された無端チェーン75bのリンクプレートに取付けたサポートを介してチェーン75bに取付けられ、掻上げレーキ76の端部がバースクリーン73の開口部を貫通して延び、ゴムや樹脂等の比重の小さな粗大物を掻き上げるように構成されている。   The rake 76 is attached to the chain 75b via a support attached to the link plate of the endless chain 75b wound around the sprocket 75a, and the end of the rake 76 passes through the opening of the bar screen 73. It is configured to extend and scrape coarse materials having a small specific gravity such as rubber and resin.

メッシュコンベア72の上方には比重の小さな粗大物がメッシュコンベア72で排出されないように、メッシュスクリーン74が水面から突出するように配置されている。   Above the mesh conveyor 72, a mesh screen 74 is disposed so as to protrude from the water surface so that coarse objects having a small specific gravity are not discharged by the mesh conveyor 72.

メッシュコンベア72には、裏面から搬送面上に向けて散気する散気ノズル77が設けられ、投入された処理対象物のうち粉粒体は散気により沈降しない程度に攪拌されながら洗浄される。このような散気により、洗浄水槽7に充填された洗浄水の上層では紙面右から左に向けて水が流れるように調整されている。   The mesh conveyor 72 is provided with an aeration nozzle 77 that diffuses from the back surface toward the transport surface, and the granular material of the input processing target is washed while being stirred to such an extent that it does not settle due to the aeration. . By such a diffuser, the upper layer of the cleaning water filled in the cleaning water tank 7 is adjusted so that the water flows from the right side to the left side of the drawing.

バースクリーン73を通過した粉粒体は分級槽7bで微粒物と中粒物に分級される。つまり、沈降速度の小さい微粒物は溢流部79から上澄水とともに排出され、沈降速度の大きい中粒物は沈殿して洗浄水槽7の底部に設けた引抜部78から排出される。   The granular material that has passed through the bar screen 73 is classified into fine particles and medium particles in the classification tank 7b. That is, the fine particles having a low sedimentation speed are discharged from the overflow portion 79 together with the supernatant water, and the medium particles having a high sedimentation speed are settled and discharged from the drawing portion 78 provided at the bottom of the washing water tank 7.

メッシュコンベア72及び掻上げ装置75の上方から選別された粗大物に洗浄水が供給されて洗浄されるとともに、溢流部79から溢流した洗浄水が追加供給される。   Washing water is supplied to the coarse material selected from above the mesh conveyor 72 and the scraping device 75 to be washed, and the overflowing washing water is additionally supplied from the overflow portion 79.

このような湿式選別手段により、比重差によって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、沈降速度差によって粉粒体が微粒物と微粒物より粒径が大きい中粒物とに分級されるようになる。   By such wet sorting means, a coarse product is sorted into a coarse product with a large specific gravity and a coarse product with a low specific gravity due to a difference in specific gravity, and a granular product with a larger particle size than a fine product and a fine product with a difference in sedimentation speed. And will be classified.

以上説明した粉粒体処理システムの構成要素となる湿式選別手段、第一の再洗浄手段、第二の再洗浄手段等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。   Specific configurations of the wet sorting means, the first recleaning means, the second recleaning means, and the like, which are components of the granular material processing system described above, are not limited to the description of the embodiment, and the present invention. Needless to say, the design can be changed as appropriate within the range where the effects of the above are achieved.

本発明による粉粒体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 selection means used for the granular material processing system by this invention 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 本発明による粉粒体処理システムの説明図Explanatory drawing of the granular material processing system by this invention 本発明による粉粒体処理システムのブロック説明図Block explanatory drawing of the granular material processing system by this invention 本発明による粉粒体処理システムのブロック説明図Block explanatory drawing of the granular material processing system by this invention 本発明による粉粒体処理システムのブロック説明図Block explanatory drawing of the granular material processing system by this invention 別実施形態の湿式選別手段の説明図Explanatory drawing of the wet-sorting means of another embodiment 別実施形態の湿式選別手段の要部の説明図Explanatory drawing of the principal part of the wet-sorting means of another embodiment

1:粉粒体処理システム
2:湿式選別手段
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:洗浄水槽
21:脈動洗浄槽
22:コンベアベルト
23a、23b、23c、23d:水噴射ノズル
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: Granule treatment system 2: Wet sorting means 4: First recleaning means 6: Second recleaning means 8: First circulation path 9: Second circulation path 20: Washing water tank 21: Pulsating washing Tank 22: Conveyor belts 23a, 23b, 23c, 23d: Water injection nozzle 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 (8)

粗大物が混入した粉粒状の焼却灰を洗浄して該焼却灰に混入し、資源として再利用する際に障害となる塩素を除去する粉粒体処理システムであって、
前記粗大物が混入した焼却灰を洗浄しながら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焼却灰を塩素含有量が相対的に多い微粒物と、微粒物より粒径が大きい塩素含有量が相対的に少ない中粒物とを含む二以上の群に分級する湿式選別手段と、
前記微粒物を再洗浄する第一の再洗浄手段と、前記中粒物を再洗浄する第二の再洗浄手段と、前記第一の再洗浄手段から排出された塩素含有量が相対的に多い洗浄排水を前記湿式選別手段へ返送する第一の循環経路と、前記第二の再洗浄手段から排出された塩素含有量が相対的に少ない洗浄排水を前記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ことを特徴とする粉粒体処理システム。
A granular processing system for cleaning granular incineration ash mixed with coarse materials, mixing in the incineration ash, and removing chlorine that becomes an obstacle when reused as a resource ,
While washing the incinerated ash mixed with the coarse product, 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, and the incinerated ash is a fine product with a relatively high chlorine content by the difference in sedimentation speed And a wet sorting means for classifying into two or more groups including a medium-sized product having a relatively small chlorine content and a particle size larger than that of the fine product,
The first re-cleaning means for re-cleaning the fine particles, the second re-cleaning means for re-cleaning the medium particles, and the chlorine content discharged from the first re-cleaning means is relatively large. A first circulation path for returning cleaning wastewater to the wet sorting means, and a first circulation path for returning cleaning wastewater having a relatively low chlorine content discharged from the second rewashing means to the second rewashing means. A granular material processing system comprising two circulation paths and reusing the washing wastewater returned through each circulation path as washing water .
前記第一の再洗浄手段は、前記微粒物を濃縮する濃縮装置と、前記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、前記濃縮装置によって分離された分離液を前記第一の循環経路を介して前記湿式選別手段へ返送することを特徴とする請求項記載の粉粒体処理システム。 The first re-washing means includes a concentrating device for concentrating the fine particles, and a washing and dehydrating device for washing and dehydrating the fine particles concentrated by the concentrating device, and the separation liquid separated by the concentrating device 2. The granular material processing system according to claim 1 , wherein the powder is returned to the wet sorting means through one circulation path. 前記第二の再洗浄手段は、前記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ことを特徴とする請求項1または2記載の粉粒体処理システム。 The second re-cleaning means includes a classification device that classifies the medium particles into coarse particles and fine particles, and a cleaning device that re-cleans the classified fine particles. Item 3. A granular material processing system according to Item 1 or 2 . 前記洗浄装置は、前記細粒物の中継槽と、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、前記第二の循環経路は前記洗浄槽からの洗浄排水を前記中継槽へ返送する循環経路と、前記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ことを特徴とする請求項記載の粉粒体処理システム。 The cleaning apparatus includes a relay tank for the fine particles, a solid-liquid separator for solid-liquid separation of the re-washed fine particles, and a cleaning tank for cleaning the fine particles separated into solid and liquid, The second circulation path includes a circulation path for returning cleaning wastewater from the cleaning tank to the relay tank, and a circulation path for returning wastewater of the solid-liquid separator to the classification device. Item 4. The granular material processing system according to Item 3 . 前記中継槽と前記固液分離機が複数段直列に配置され、前記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、前記洗浄槽の排水を前記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前記分級装置へ返送する循環経路を備えていることを特徴とする請求項記載の粉粒体処理システム。 The relay tank and the solid-liquid separator are arranged in a plurality of stages in series, and the second circulation path is a circulation path for transferring the waste water of the subsequent solid-liquid separator to the relay tank immediately before the previous solid-liquid separator; And a circulation path for transferring waste water from the washing tank to a relay tank immediately before the washing tank, and a circulation path for returning waste water from the first-stage solid-liquid separator to the classification device. Item 5. The granular material processing system according to Item 4 . 粗大物が混入した粉粒状の焼却灰を洗浄して該焼却灰に混入し、資源として再利用する際に障害となる塩素を除去する粉粒体処理方法であって、
前記粗大物が混入した焼却灰を洗浄しながら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焼却灰を塩素含有量が相対的に多い微粒物と、微粒物より粒径が大きい塩素含有量が相対的に少ない中粒物とを含む二以上の群に分級する分級工程とを含む湿式選別工程と、
前記微粒物を再洗浄する第一の再洗浄工程と、前記中粒物を再洗浄する第二の再洗浄工程と、前記第一の再洗浄工程から排出された塩素含有量が相対的に多い洗浄排水を前記湿式選別工程へ返送する第一の循環工程と、前記第二の再洗浄工程から排出された塩素含有量が相対的に少ない洗浄排水を前記第二の再洗浄工程へ返送する第二の循環工程を備え、それぞれの循環工程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ことを特徴とする粉粒体処理方法。
It is a granular treatment method for cleaning granular incineration ash mixed with coarse substances, mixing in the incineration ash, and removing chlorine that becomes an obstacle when reusing as a resource ,
A specific gravity sorting process for sorting the coarse product into a coarse product with a large specific gravity and a coarse product with a low specific gravity by cleaning the incinerated ash mixed with the coarse product, and a relative chlorine content in the incinerated ash by the difference in sedimentation speed. A wet sorting step including a classification step of classifying into two or more groups including a large amount of fine particles and a medium particle having a relatively small chlorine content and a particle size larger than the fine particles,
The first rewashing step for rewashing the fine particles, the second rewashing step for rewashing the medium particles, and the chlorine content discharged from the first rewashing step is relatively high. A first circulation step for returning the washing wastewater to the wet sorting step, and a first circulation step for returning the washing wastewater having a relatively small chlorine content discharged from the second rewashing step to the second rewashing step. A method for treating a granular material , comprising two circulation steps, wherein the washing wastewater returned through each circulation step is reused as washing water .
前記第一の再洗浄工程は、前記微粒物を濃縮する濃縮工程と、前記濃縮工程によって濃縮された微粒物を洗浄脱水する洗浄脱水工程を備え、前記濃縮工程によって分離された分離液を前記第一の循環工程により前記湿式選別工程へ返送することを特徴とする請求項6記載の粉粒体処理方法。The first re-washing step includes a concentration step for concentrating the fine particles, and a washing and dehydration step for washing and dewatering the fine particles concentrated in the concentration step, and the separated liquid separated in the concentration step is It returns to the said wet selection process by one circulation process, The granular material processing method of Claim 6 characterized by the above-mentioned. 前記第二の再洗浄工程は、前記中粒物を粗粒物と細粒物に分級する分級工程と、分級された細粒物を再洗浄する洗浄工程を備えていることを特徴とする請求項6または7記載の粉粒体処理方法。The second re-cleaning step includes a classification step for classifying the medium-sized product into a coarse-grained product and a fine-grained product, and a cleaning step for re-cleaning the classified fine-grained product. Item 6. A method for treating a granular material according to Item 6 or 7.
JP2007319104A 2007-12-11 2007-12-11 Powder processing system and powder processing method Active JP4943309B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2007319104A JP4943309B2 (en) 2007-12-11 2007-12-11 Powder processing system and powder processing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2007319104A JP4943309B2 (en) 2007-12-11 2007-12-11 Powder processing system and powder processing method

Related Child Applications (1)

Application Number Title Priority Date Filing Date
JP2008054171A Division JP4943358B2 (en) 2008-03-04 2008-03-04 Powder processing system and powder processing method

Publications (2)

Publication Number Publication Date
JP2009136846A JP2009136846A (en) 2009-06-25
JP4943309B2 true JP4943309B2 (en) 2012-05-30

Family

ID=40868054

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2007319104A Active JP4943309B2 (en) 2007-12-11 2007-12-11 Powder processing system and powder processing method

Country Status (1)

Country Link
JP (1) JP4943309B2 (en)

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5409404B2 (en) * 2010-01-08 2014-02-05 三菱重工環境・化学エンジニアリング株式会社 Incineration ash treatment apparatus and incineration ash treatment method
JP5783547B2 (en) * 2010-03-25 2015-09-24 三菱重工環境・化学エンジニアリング株式会社 Incineration ash treatment system
JP5904123B2 (en) * 2011-05-31 2016-04-13 東レ株式会社 Method and apparatus for cleaning and separating mixed materials
JP2013124960A (en) * 2011-12-15 2013-06-24 Shimizu Corp Treatment method of cesium-contaminated soil
JP5983992B2 (en) * 2012-05-15 2016-09-06 清水建設株式会社 Cleaning treatment method for cesium contaminated soil
JP6198617B2 (en) * 2013-02-27 2017-09-20 太平洋セメント株式会社 Method and apparatus for converting waste incineration ash into cement raw material
JP6433214B2 (en) * 2014-09-24 2018-12-05 太平洋セメント株式会社 Method and apparatus for desalination of mixed ash and raw material for cement
CN108889706B (en) * 2018-08-14 2024-03-19 连云港瑞隆预拌砂浆有限公司 Raw material stone cleaning and grading device for producing concrete pipe piles

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6083055A (en) * 1983-10-12 1985-05-11 Ricoh Co Ltd Record density controlling device
JPS6233564A (en) * 1985-08-08 1987-02-13 Tsukishima Kikai Co Ltd Method and apparatus for treating contaminated grit
US5128068A (en) * 1990-05-25 1992-07-07 Westinghouse Electric Corp. Method and apparatus for cleaning contaminated particulate material
JP2501769B2 (en) * 1993-11-22 1996-05-29 株式会社エコーテック Jig sorting method for crushed material and apparatus therefor
JP2001149913A (en) * 1999-11-24 2001-06-05 Shimizu Corp Cleaning method of contaminated soil
JP2005081247A (en) * 2003-09-09 2005-03-31 Mitsubishi Heavy Ind Ltd Apparatus for cleaning contaminated soil
JP2006035103A (en) * 2004-07-27 2006-02-09 Mitsui Mining & Smelting Co Ltd Heavy metal-contaminated soil treatment system and heavy metal-contaminated soil treating method

Also Published As

Publication number Publication date
JP2009136846A (en) 2009-06-25

Similar Documents

Publication Publication Date Title
JP4943309B2 (en) Powder processing system and powder processing method
JP5481034B2 (en) Incineration ash treatment method and incineration ash treatment equipment
JP5292483B2 (en) Wet sorting device
JP2010227827A (en) System and method for treating granule
JP4798619B2 (en) Sand separation and cleaning equipment
JP4678627B2 (en) Cleaning processing method and cleaning processing apparatus
JP5292482B2 (en) Wet sorting device
JP4931841B2 (en) Wet sorting device
JP5143070B2 (en) Powder processing system and powder processing method
JP5351986B2 (en) Powder processing system and powder processing method
RU2571112C2 (en) Loose material mobile cleaner plant
JP4943358B2 (en) Powder processing system and powder processing method
JP2010227826A (en) System and method for treating granule
JP2010234217A (en) Powdery particle material treatment system, and powdery particle material treatment method
JPS6233564A (en) Method and apparatus for treating contaminated grit
JP4633502B2 (en) Sand separation and cleaning equipment
CA3142284C (en) Method and apparatus for treating contaminated particulate material
US4584094A (en) Method and apparatus for reclaiming coal
SU1417789A3 (en) Apparatus for separating various components of product in heavy suspension
JP2006095413A (en) Sand separation/washing device
NL9001210A (en) Soil and mud purifying method - using counter-flow drum with inner slanting, fixed scoops
KR100699492B1 (en) A Cleaning and Sorting Device Of Building Waste
RU2731986C1 (en) Hydroseparator of solid domestic wastes (sdw) for separation of sdw in water flow passing through apparatus
KR200381994Y1 (en) A Cleaning and Sorting Device Of Building Waste
JPS6233563A (en) Cleaning method for contaminated grit containing waste

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20100917

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20110909

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20110913

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20111114

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20120131

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20120229

R150 Certificate of patent or registration of utility model

Ref document number: 4943309

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20150309

Year of fee payment: 3