JP2014070997A - Soil continuous processing system - Google Patents

Soil continuous processing system Download PDF

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JP2014070997A
JP2014070997A JP2012216933A JP2012216933A JP2014070997A JP 2014070997 A JP2014070997 A JP 2014070997A JP 2012216933 A JP2012216933 A JP 2012216933A JP 2012216933 A JP2012216933 A JP 2012216933A JP 2014070997 A JP2014070997 A JP 2014070997A
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soil
fine
water
slurry
grained
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Ichiro Asakura
一郎 朝倉
Takashi Inai
隆 稲井
Saneji Hirato
實治 平戸
Tadahiro Fujii
忠広 藤井
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DOJO KANKYO PROCESS KENKYUSHO KK
IHI Corp
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DOJO KANKYO PROCESS KENKYUSHO KK
IHI Corp
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Abstract

PROBLEM TO BE SOLVED: To make it possible to separate and treat an enormous amount of removed soils in a short time.SOLUTION: A soil continuous processing system includes: a slurry generating device 5 which mixes the mixed soil containing coarse grain soil whose radiation level is low and fine grain soil whose radiation level is high and grain size is smaller than that of the coarse grain soil with water sprayed from a spray nozzle; a sedimentation separator 6 which separates slurry into the coarse grain soil and suspension water containing the fine grain soil by sedimentation; and a flocculation and separation apparatus 11 which adds a flocculant to the suspension water to perform flocculation and separation of the fine grain soil.

Description

本発明は、土壌連続処理システムに関するものである。   The present invention relates to a soil continuous treatment system.

除染作業によって集められた除去土壌には、草、木及び落ち葉等の可燃物や、瓦礫等の不燃物が含まれている。また、除染土壌には、放射能レベルが低い粗粒土や放射能レベルが高い細粒土が含まれている。長期間に亘って放射性物質が貯蔵される中間貯蔵施設においては、貯蔵物ごとに放射能レベルを把握し、焼却減容できる可燃物を取り除いた上で貯蔵物の放射能レベルに応じた管理を行う必要がある。ところが、上述のように様々なものが含まれる除染土壌を収容容器に入れると、収容容器の内部において放射性物質の濃度が不均一となり、当該収容容器の管理が困難となる。また、混在する有機物の腐敗よる有毒ガスや火災を防止する必要もある。このため、除去土壌については、中間貯蔵施設に搬入する前に、受入及び分別施設等において、放射能レベルや可燃あるいは不燃の種別に応じた分別処理が必要となる。   The removed soil collected by the decontamination work includes combustible materials such as grass, trees and fallen leaves, and non-combustible materials such as rubble. In addition, the decontaminated soil includes coarse soil having a low radioactivity level and fine soil having a high radioactivity level. At intermediate storage facilities where radioactive materials are stored for a long period of time, the level of radioactivity is ascertained for each stored item, and after removing combustibles that can be reduced by incineration, management according to the radioactive level of the stored item is performed. There is a need to do. However, when decontaminated soil containing various things as described above is placed in the storage container, the concentration of the radioactive substance in the storage container becomes non-uniform, making it difficult to manage the storage container. In addition, it is necessary to prevent toxic gas and fire due to the decay of mixed organic matter. For this reason, about removal soil, before carrying in to an intermediate | middle storage facility, in a reception and separation facility etc., the separation process according to the radioactivity level or the type of combustible or incombustible is needed.

例えば、特許文献1には、除染土壌の分別処理にあたり、除去土壌の洗浄を行うことができる装置が記載されている。このような装置を用いることによって、除去土壌に含まれる油分等の不要成分を除去することができる。除去土壌の分別は、このような特許文献1に示すような装置を用いながら行うことになる。   For example, Patent Document 1 describes an apparatus capable of cleaning removed soil in the separation treatment of decontaminated soil. By using such an apparatus, unnecessary components such as oil contained in the removed soil can be removed. The separation of the removed soil is performed using such an apparatus as shown in Patent Document 1.

特開2010−284624号公報JP 2010-284624 A

しかしながら、特許文献1に示される装置がそうであるように、現在のところ、除去土壌の分別処理を行うために用いられる装置は、各々が独立している。このため、除去土壌の分別処理は、バッチ処理を行うことしかできず、連続処理を行うことができない。現在、発生している除去土壌は、膨大な量である。このため、バッチ処理では、多大な時間と費用が必要となる。また、バッチ処理では、各装置間における移送作業等を作業者が手作業にて行うことになり、作業者の放射線被曝量が多くなってしまう。   However, as is the case with the device disclosed in Patent Document 1, at present, the devices used for performing the separation treatment of the removed soil are independent of each other. For this reason, the separation treatment of the removed soil can only perform batch processing, and cannot perform continuous processing. Currently, there is a huge amount of removed soil generated. For this reason, a lot of time and cost are required in batch processing. Further, in batch processing, the transfer work between the apparatuses is manually performed by the worker, and the radiation exposure amount of the worker increases.

本発明は、上述する問題点に鑑みてなされたもので、膨大な量の除去土壌を短時間で分別処理可能とすることを目的とする。   The present invention has been made in view of the above-described problems, and an object thereof is to enable a huge amount of removed soil to be separated in a short time.

本発明は、上記課題を解決するための手段として、以下の構成を採用する。   The present invention adopts the following configuration as means for solving the above-described problems.

第1の発明は、土壌連続処理システムであって、放射能レベルが低い粗粒土と放射能レベルが高くかつ上記粗粒土よりも粒径の小さい細粒土とを含む混合土を、噴射ノズルより噴射した水と混合してスラリーを生成するスラリー生成装置と、上記スラリーを沈降分離により上記粗粒土と上記細粒土を含む懸濁水とに分離する沈降分離機と、上記懸濁水に凝集剤を添加して上記細粒土を凝集させて分離する凝集分離装置とを備えるという構成を採用する。   1st invention is a soil continuous processing system, Comprising: The mixed soil containing a coarse-grained soil with a low radioactivity level and a fine-grained soil with a high radioactivity level and a particle size smaller than the said coarse-grained soil is injected. A slurry generator that mixes with water sprayed from a nozzle to generate a slurry, a settling separator that separates the slurry into the coarse-grained soil and the suspended water containing the fine-grained soil by sedimentation, and the suspended water A configuration is adopted in which a flocculant is added to the flocculent separation device for aggregating and separating the fine-grained soil.

第2の発明は、上記第1の発明において、上記沈降分離機から排出される懸濁水を一時的に貯留して上記凝集分離装置に供給する濁水槽をさらに備えるという構成を採用する。   The second invention adopts a configuration in the first invention, further comprising a muddy water tank for temporarily storing the suspended water discharged from the sedimentation separator and supplying the suspended water to the coagulation separator.

第3の発明は、上記第2の発明において、上記濁水槽に貯留された上記懸濁水を攪拌する攪拌装置を備えるという構成を採用する。   3rd invention employ | adopts the structure provided with the stirring apparatus which stirs the said suspension water stored in the said muddy water tank in the said 2nd invention.

第4の発明は、上記第2または第3の発明において、上記濁水槽の容量が、上記凝集分離装置で分離された細粒土が詰められる収容容器の容量以上であるという構成を採用する。   According to a fourth aspect of the present invention, in the second or third aspect of the invention, the capacity of the turbid water tank is equal to or greater than the capacity of the storage container filled with the fine-grained soil separated by the coagulation / separation apparatus.

本発明によれば、スラリー生成装置において放射能レベルが低い粗粒土と放射能レベルが高い細粒土とを含むスラリーが生成され、このスラリーが沈降分離機において粗粒土と細粒土を含む懸濁水とに分離され、凝集分離装置において懸濁水に凝集剤が添加されて細粒土が分離される。つまり、本発明によれば、放射能レベルが低い粗粒土と放射能レベルが高い細粒土とを連続的に分離することができる。したがって、本発明によれば、膨大な量の除去土壌を短時間で分別処理することができる。   According to the present invention, a slurry containing a coarse-grained soil having a low radioactivity level and a fine-grained soil having a high radioactivity level is produced in the slurry generator, and the slurry is separated into coarse-grained soil and fine-grained soil in a settling separator. In the flocculating / separating apparatus, a flocculant is added to the suspending water to separate the fine-grained soil. That is, according to the present invention, it is possible to continuously separate coarse-grained soil having a low radioactivity level and fine-grained soil having a high radioactivity level. Therefore, according to the present invention, a huge amount of removed soil can be separated in a short time.

本発明の一実施形態における土壌連続処理システム1の概略構成を示したフロー図である。It is the flowchart which showed schematic structure of the soil continuous processing system 1 in one Embodiment of this invention. 本発明の一実施形態における土壌連続処理システム1の動作を説明するためのフローチャートである。It is a flowchart for demonstrating operation | movement of the soil continuous processing system 1 in one Embodiment of this invention.

以下、図面を参照して、本発明に係る土壌連続処理システムの一実施形態について説明する。なお、以下の図面において、各部材を認識可能な大きさとするために、各部材の縮尺を適宜変更している。   Hereinafter, an embodiment of a soil continuous treatment system according to the present invention will be described with reference to the drawings. In the following drawings, the scale of each member is appropriately changed in order to make each member a recognizable size.

図1は、本実施形態の土壌連続処理システム1の概略構成を示したフロー図である。この図に示すように、本実施形態の土壌連続処理システム1は、振動篩機2、第1ベルトコンベア3、ホッパ4、スラリー生成装置5、沈降分離機6、第1スクリューコンベア7、第2ベルトコンベア8、濁水槽9、濁水ポンプ10、凝集分離装置11、第2スクリューコンベア12、収容箱13、返送ポンプ14、水槽15、低圧ポンプ16及び高圧ポンプ17を備えている。   FIG. 1 is a flowchart showing a schematic configuration of a soil continuous treatment system 1 of the present embodiment. As shown in this figure, the soil continuous processing system 1 of the present embodiment includes a vibrating screen 2, a first belt conveyor 3, a hopper 4, a slurry generator 5, a sedimentation separator 6, a first screw conveyor 7, and a second. A belt conveyor 8, a muddy water tank 9, a muddy water pump 10, a flocculation / separation device 11, a second screw conveyor 12, a storage box 13, a return pump 14, a water tank 15, a low pressure pump 16 and a high pressure pump 17 are provided.

振動篩機2は、除去土壌そのものである原土X1に対して振動を付与することによって、原土X1を、分別土X2(混合土)と、可燃物X3と、不燃物X4とに分別する。ここで、分別土X2は、放射能レベルが低い粗粒土(粒径がおおよそミリオーダの砂状の土)と、粗粒土よりも粒径が小さく放射能レベルが高い細粒土(粒径がおおよそミクロンオーダの粉末状の土)とを含む混合土である。このような振動篩機2によって、放射性物質を含む分別土X2と、焼却減容が可能な可燃物X3及び不燃物X4とに分離される。   The vibration sieving machine 2 separates the raw soil X1 into the separated soil X2 (mixed soil), the combustible material X3, and the incombustible material X4 by applying vibration to the raw soil X1 that is the removed soil itself. . Here, the fractionated soil X2 includes a coarse-grained soil having a low radioactivity level (sandy soil having a particle size of approximately milliorder) and a fine-grained soil having a smaller particle size and a higher radioactivity level (grain size). Is a mixed soil including a powdery soil of approximately micron order. Such a vibrating sieve 2 separates the separated soil X2 containing the radioactive material into the combustible material X3 and the incombustible material X4 that can be incinerated and reduced in volume.

可燃物X3は草、木及び落ち葉等からなり、不燃物は付着土壌や礫類からなる。この振動篩機2では、必ずしも可燃物X3と不燃物X4とを分別する必要はない。つまり、可燃物X3と不燃物X4とを別のスラリー生成装置にて分別することも可能である。   The combustible material X3 is made of grass, trees, and fallen leaves, and the incombustible material is made of attached soil or gravel. In the vibrating screen 2, it is not always necessary to separate the combustible material X3 and the non-combustible material X4. That is, the combustible material X3 and the non-combustible material X4 can be separated by another slurry generator.

第1ベルトコンベア3は、振動篩機2の下流側に配置されており、振動篩機2から排出される分別土X2を連続的に搬送し、ホッパ4に供給する。ホッパ4は、第1ベルトコンベア3の下流側に配置されており、第1ベルトコンベア3によって搬送されてきた分別土X2を一時的に貯留すると共に、当該分別土X2を連続的にスラリー生成装置5に定量供給する。スラリー生成装置5は、ホッパ4の下流側に配置されており、第1ベルトコンベア3から供給される分別土X2を噴射ノズルから噴射した水と共に衝突板に衝突させてスラリーX5を生成する。このスラリー生成装置5については、例えば特開2010−284624号公報に詳細に記載されているため、ここでの詳しい説明については省略するが、高圧ポンプ17から圧送される高圧水を噴射ノズルから噴射すると共に、低圧ポンプ16から圧送される同伴水として高圧水に沿って噴射し、これらの水に対して分別土X2を供給し、高速噴射された水よる衝撃波及び衝突板に衝突させることでスラリーX5を生成する。このようなスラリー生成装置5によれば、粗粒土及び細粒土が高速に噴射された水により発生する衝撃波や衝突板に衝突させられること等によって水の中に分散され、これによって分別土X2中に存在する細粒魂を粉砕する。また、スラリー生成装置5では、粗粒土及び細粒土が高速に噴射された水により発生する衝撃波および衝突板に衝突させられることによって粗粒土及び細粒土の研磨が行われる。   The first belt conveyor 3 is disposed on the downstream side of the vibration sieve device 2, continuously conveys the sorted soil X <b> 2 discharged from the vibration sieve device 2, and supplies it to the hopper 4. The hopper 4 is arranged on the downstream side of the first belt conveyor 3, temporarily stores the sorted soil X2 conveyed by the first belt conveyor 3, and continuously generates the sorted soil X2 in a slurry generator. Quantitative supply to 5. The slurry generating device 5 is disposed on the downstream side of the hopper 4, and generates the slurry X5 by causing the separation soil X2 supplied from the first belt conveyor 3 to collide with the collision plate together with water sprayed from the spray nozzle. Since the slurry generator 5 is described in detail in, for example, Japanese Patent Application Laid-Open No. 2010-284624, detailed description thereof is omitted here, but high-pressure water pumped from the high-pressure pump 17 is injected from the injection nozzle. At the same time, it is sprayed along the high-pressure water as the entrained water pumped from the low-pressure pump 16, the separation soil X2 is supplied to these waters, and the slurry is caused to collide with the shock wave and the collision plate caused by the high-speed sprayed water. X5 is generated. According to such a slurry production | generation apparatus 5, a coarse-grained soil and a fine-grained soil are disperse | distributed in water by making it collide with the shock wave and collision board which generate | occur | produce with the water injected at high speed, and, thereby, classification soil Crush the fine soul that exists in X2. Moreover, in the slurry production | generation apparatus 5, coarse-grained soil and fine-grained soil are grind | polished by making a coarse-grained soil and fine-grained soil collide with the shock wave and collision board which generate | occur | produce with the water injected at high speed.

沈降分離機6は、スラリー生成装置5の下流側に配置されており、スラリー生成装置5から供給されるスラリーX5を沈降分離することによって、粗粒土X6と細粒土を含む懸濁水X7とに分離する。この沈降分離機6は、例えば、粗粒土の沈降速度より遅く、細粒土の沈降速度よりも速い上昇流を沈降分離機6の内部に形成し、細粒土を含む上澄み液を懸濁水X7として排出し、底部に沈殿する沈降物を粗粒土X6として排出する。   The sedimentation separator 6 is disposed on the downstream side of the slurry generator 5, and by sedimenting and separating the slurry X5 supplied from the slurry generator 5, the coarse soil X6 and the suspended water X7 containing the fine soil To separate. The sedimentation separator 6 forms, for example, an upward flow in the sedimentation separator 6 that is slower than the sedimentation speed of the coarse-grained soil and faster than the sedimentation speed of the fine-grained soil, and the supernatant liquid containing the fine-grained soil is suspended in the suspended water. The sediment which is discharged as X7 and settles at the bottom is discharged as coarse-grained soil X6.

第1スクリューコンベア7は、沈降分離機6の粗粒土X6の排出口と接続されており、沈降分離機6から排出された粗粒土X6を斜め上方に向けて搬送し、液分を残して固相分のみを取り出す。第2ベルトコンベア8は、第1スクリューコンベア7の下流側に配置されており、第1スクリューコンベア7から排出された粗粒土X6を例えばトラック等まで搬送する。   The 1st screw conveyor 7 is connected with the discharge port of the coarse grain soil X6 of the sedimentation separator 6, conveys the coarse grain soil X6 discharged | emitted from the sedimentation separator 6 diagonally upward, and leaves a liquid component. Remove only the solid phase. The 2nd belt conveyor 8 is arrange | positioned in the downstream of the 1st screw conveyor 7, and conveys the coarse grain soil X6 discharged | emitted from the 1st screw conveyor 7 to a truck etc., for example.

濁水槽9は、沈降分離機6の懸濁水X7の排出口と接続されており、貯留槽9aと、攪拌装置9bとを備えている。貯留槽9aは、懸濁水X7を一時的に貯留する容器である。攪拌装置9bは、貯留槽9a内部に貯留された懸濁水X7を攪拌するものである。なお、本実施形態においては、貯留槽9aの容量は、収容箱13に蓄積される細粒土X8が収容される収容容器の容量以上とされている。すなわち、このような濁水槽9は、沈降分離機6から排出される懸濁水X7を一時的に貯留すると共に貯留中に攪拌する。   The muddy water tank 9 is connected to the discharge port of the suspended water X7 of the sedimentation separator 6, and includes a storage tank 9a and a stirring device 9b. The storage tank 9a is a container that temporarily stores the suspended water X7. The stirring device 9b stirs the suspension water X7 stored in the storage tank 9a. In the present embodiment, the capacity of the storage tank 9a is equal to or greater than the capacity of the storage container in which the fine soil X8 accumulated in the storage box 13 is stored. That is, such a muddy water tank 9 temporarily stores the suspended water X7 discharged from the sedimentation separator 6 and stirs it during the storage.

濁水ポンプ10は、濁水槽9に接続されており、濁水槽9に貯留された懸濁水X7を凝集分離装置11に向けて圧送する。凝集分離装置11は、濁水ポンプ10の下流側に配置されており、下流側から順に配列される凝集剤添加装置11a、凝集反応管11b及び遠心分離脱水機11cを備えている。凝集剤添加装置11aは懸濁水X7に凝集剤を添加する。凝集反応管11bは凝集剤が添加された懸濁水X7を貯留して懸濁水X7に含まれる細粒土X8が凝集するまでの間、懸濁水X7を一時的に貯留する。遠心分離脱水機11cは、懸濁水X7を細粒土X8と水X9とに分離する。すなわち、このような凝集分離装置11は、懸濁水X7に凝集剤を添加して細粒土X8を凝集させて分離する。   The muddy water pump 10 is connected to the muddy water tank 9 and pumps the suspension water X7 stored in the muddy water tank 9 toward the flocculating / separating device 11. The aggregating / separating device 11 is disposed on the downstream side of the muddy water pump 10 and includes an aggregating agent adding device 11a, an aggregating reaction tube 11b, and a centrifugal dehydrator 11c arranged in order from the downstream side. The flocculant adding device 11a adds the flocculant to the suspension water X7. The agglomeration reaction tube 11b temporarily stores the suspension water X7 until the suspension water X7 to which the aggregating agent is added and the fine soil X8 contained in the suspension water X7 aggregates. The centrifugal dehydrator 11c separates the suspended water X7 into fine-grained soil X8 and water X9. That is, such a flocculating / separating apparatus 11 adds a flocculant to the suspension water X7 to flocculate and separate the fine-grained soil X8.

第2スクリューコンベア12は、凝集分離装置11の下流側に配置されており、凝集分離装置11から排出された細粒土X8を斜め上方に向けて搬送し、液分を残して固相分のみを取り出す。収容箱13は、第2スクリューコンベア12の下流側に配置されており、第2スクリューコンベア12から排出された細粒土X8を一時的に収容する放射線の遮蔽効果を有する容器である。   The second screw conveyor 12 is disposed on the downstream side of the aggregating / separating apparatus 11 and conveys the fine-grained soil X8 discharged from the aggregating / separating apparatus 11 obliquely upward, leaving only the liquid component and only the solid phase component. Take out. The storage box 13 is a container having a radiation shielding effect that is disposed downstream of the second screw conveyor 12 and temporarily stores the fine-grained soil X8 discharged from the second screw conveyor 12.

返送ポンプ14は、凝集分離装置11から排出された水X9を水槽15に向けて圧送するためのポンプであり、凝集分離装置11と水槽15との間に配置されている。水槽15は、返送ポンプ14より圧送された水X9を一時的に貯留する。低圧ポンプ16は、凝集分離装置11から水槽15に向けて流れる水X9の一部を高圧ポンプ17よりも低圧にてスラリー生成装置5に圧送するポンプである。この低圧ポンプ16によって圧送される水X9がスラリー生成装置5において上記同伴水となる。高圧ポンプ17は、水槽15に貯留された水X9を低圧ポンプ16よりも高圧にてスラリー生成装置5に圧送するポンプである。本実施形態の土壌連続処理システム1では、これらの返送ポンプ14、水槽15、低圧ポンプ16及び高圧ポンプ17によって、遠心分離脱水機11cで回収されたスラリー生成装置5で使用した水を再度スラリー生成装置5に供給する構成となっており、水の大半を循環させるシステムとなっている。このため、土壌連続処理システム1の外部への排水を最小限に抑えることができ、環境汚染の拡大の可能性を最小限に抑えることができる。   The return pump 14 is a pump for pumping the water X9 discharged from the coagulation / separation apparatus 11 toward the water tank 15, and is disposed between the coagulation / separation apparatus 11 and the water tank 15. The water tank 15 temporarily stores the water X9 pumped by the return pump 14. The low-pressure pump 16 is a pump that pumps a part of the water X9 flowing from the coagulation / separation device 11 toward the water tank 15 to the slurry generation device 5 at a lower pressure than the high-pressure pump 17. The water X9 pumped by the low-pressure pump 16 becomes the entrained water in the slurry generator 5. The high-pressure pump 17 is a pump that pumps the water X 9 stored in the water tank 15 to the slurry generator 5 at a higher pressure than the low-pressure pump 16. In the soil continuous treatment system 1 of this embodiment, the return pump 14, the water tank 15, the low-pressure pump 16, and the high-pressure pump 17 generate slurry again from the water used in the slurry generator 5 collected by the centrifugal dehydrator 11c. The system is configured to supply to the device 5 and is a system that circulates most of the water. For this reason, drainage to the outside of the soil continuous treatment system 1 can be minimized, and the possibility of expansion of environmental pollution can be minimized.

なお、本実施形態の土壌連続処理システム1は、不図示の制御装置や発電装置を備えており、各装置に必要とされる電力が発電装置によって生成され、また各装置が制御装置によって制御される。   In addition, the soil continuous processing system 1 of this embodiment is provided with the control apparatus and electric power generating apparatus which are not illustrated, the electric power required for each apparatus is produced | generated by the electric power generation apparatus, and each apparatus is controlled by the control apparatus. The

続いて、このように構成された本実施形態の土壌連続処理システム1の動作について、図2のフローチャートを参照して説明する。なお、以下の動作の説明において、特に説明のない限り、その主体は制御装置である。   Then, operation | movement of the soil continuous processing system 1 of this embodiment comprised in this way is demonstrated with reference to the flowchart of FIG. In the following description of the operation, the main body is a control device unless otherwise specified.

まず、原土X1の一次分別する(ステップS1)。ここでは、原土X1を振動篩機2によって分別土X2と、可燃物X3及び不燃物X4との混合体とに分別する。なお、分別土X2は、第1ベルトコンベア3によってホッパ4に供給され、ホッパ4において一時的に蓄積される。   First, the primary sorting of the raw soil X1 is performed (step S1). Here, the raw soil X1 is separated into the separated soil X2 and the mixture of the combustible material X3 and the incombustible material X4 by the vibration sieve device 2. The sorted soil X2 is supplied to the hopper 4 by the first belt conveyor 3 and is temporarily accumulated in the hopper 4.

続いて、分別土X2に対して洗浄及び研磨を行う(ステップS2)。ここでは、スラリー生成装置5にて、ホッパ4から供給される分別土X2と、低圧ポンプ16及び高圧ポンプ17から圧送される水X9とを衝突板に衝突させることで、見かけ上粗粒土に見える細粒土魂が粉砕され、細粒土が均質に混じりあったスラリーX5を生成する。また、粗粒土X6が研磨されることにより、粗粒土表面に付着した細粒土が剥離され、細粒土がさらに均質に混じりあったスラリーX5を生成する。   Subsequently, the sorting soil X2 is cleaned and polished (step S2). Here, in the slurry generator 5, the fractionated soil X2 supplied from the hopper 4 and the water X9 pumped from the low-pressure pump 16 and the high-pressure pump 17 are collided with the collision plate, so that apparently coarse-grained soil is formed. The visible fine-grained earth soul is crushed to produce a slurry X5 in which the fine-grained soil is homogeneously mixed. Further, by polishing the coarse-grained soil X6, the fine-grained soil adhering to the surface of the coarse-grained soil is peeled off, and a slurry X5 in which the fine-grained soil is further mixed homogeneously is generated.

続いて、スラリーX5に対して分級が行われる(ステップS3)。ここでは、スラリー生成装置5から排出されたスラリーX5を沈降分離機6において沈降分離することによって、粗粒土X6と懸濁水X7とに分離する。なお、粗粒土X6は、第1スクリューコンベア7及び第2ベルトコンベア8を介してトラック等に搬送され、その後収容容器(フレコンバック)に収容される。   Subsequently, classification is performed on the slurry X5 (step S3). Here, the slurry X5 discharged from the slurry generating device 5 is separated into the coarse-grained soil X6 and the suspended water X7 by being settled and separated in the sedimentation separator 6. In addition, the coarse-grained soil X6 is conveyed to a truck etc. via the 1st screw conveyor 7 and the 2nd belt conveyor 8, and is accommodated in an accommodation container (flexible bag) after that.

続いて、懸濁水X7に対して凝集分離(ステップS4)及び脱水(ステップS5)が行われる。ここでは、沈降分離機6から排出された懸濁水X7を濁水ポンプ10で凝集分離装置11に圧送し、凝集剤添加装置11aで凝集剤を添加し、凝集反応管11bで凝集反応の進行を待ち、遠心分離脱水機11cで細粒土X8と水X9とに分離する。そして、細粒土X8は、第2スクリューコンベア12によって収容箱13やフレコンバック等の収容容器に収容される。また、水X9は、返送ポンプ14によって水槽15に圧送される。   Subsequently, flocculation separation (step S4) and dehydration (step S5) are performed on the suspension water X7. Here, the suspended water X7 discharged from the sedimentation separator 6 is pumped to the aggregating / separating device 11 by the turbid water pump 10, the aggregating agent is added by the aggregating agent adding device 11a, and the agglutination reaction tube 11b waits for the agglutination reaction to proceed. Then, the finely divided soil X8 and water X9 are separated by the centrifugal dehydrator 11c. The fine-grained soil X8 is accommodated in an accommodation container such as an accommodation box 13 or a flexible container bag by the second screw conveyor 12. The water X9 is pumped to the water tank 15 by the return pump 14.

なお、ステップS1において分離された可燃物X3及び不燃物X4との混合体に対しては、分別土X2の処理と同様の仕組みを持つ別の分別装置を用いて二次分別が行われる(ステップS6)。ここで、分離された可燃物X3は収容容器(フレコンバック)に収容される。また、不燃物は分級(ステップ3)に戻しても良い。   The mixture of the combustible material X3 and the non-combustible material X4 separated in step S1 is subjected to secondary separation using another separation device having a mechanism similar to that of the separation soil X2 (step). S6). Here, the separated combustible material X3 is accommodated in an accommodation container (flexible bag). Moreover, you may return an incombustible material to classification (step 3).

次に、このような本実施形態の土壌連続処理システム1の作用及び効果について説明する。   Next, an effect | action and effect of such a soil continuous processing system 1 of this embodiment are demonstrated.

細粒土の放射能レベルが高い原因としては、細粒土がケイ素を多く含み、ケイ素の分子構造がセシウム原子を取り込みやすく分離し難いためであると考えられる。本実施形態の土壌連続処理システム1によれば、スラリー生成装置5において放射能レベルが低い粗粒土X6と放射能レベルが高い細粒土X8とを含むスラリーX5が生成され、このスラリーX5が沈降分離機6において粗粒土X6と細粒土X8を含む懸濁水X7とに分離され、凝集分離装置11において懸濁水X7に凝集剤が添加されて細粒土X8が分離される。つまり、本実施形態の土壌連続処理システム1によれば、放射能レベルが低い粗粒土X6と放射能レベルが高い細粒土X8とを、スラリー生成装置5、沈降分離機6及び凝集分離装置11が連動することにより連続的に分離することができる。したがって、本実施形態の土壌連続処理システム1によれば、膨大な量の除去土壌(原土X1)を短時間で分別処理することができる。   The reason for the high radioactivity level of the fine-grained soil is considered to be that the fine-grained soil contains a large amount of silicon, and the molecular structure of silicon is easy to take up cesium atoms and is difficult to separate. According to the soil continuous processing system 1 of the present embodiment, the slurry generator 5 generates the slurry X5 including the coarse soil X6 having a low radioactivity level and the fine soil X8 having a high radioactivity level. The settling separator 6 separates the coarse-grained soil X6 and the suspended water X7 containing the fine-grained soil X8, and the flocculating / separating device 11 adds a flocculant to the suspended water X7 to separate the fine-grained soil X8. That is, according to the soil continuous processing system 1 of the present embodiment, the coarse-grained soil X6 with a low radioactivity level and the fine-grained soil X8 with a high radioactivity level are converted into a slurry generator 5, a sedimentation separator 6, and a coagulation separator. 11 can be continuously separated by interlocking. Therefore, according to the soil continuous processing system 1 of this embodiment, a huge amount of removed soil (raw soil X1) can be separated and processed in a short time.

さらに、本実施形態の土壌連続処理システム1によれば、スラリー生成装置5において、スラリーX5に含まれる粗粒土X6と細粒土X8とが均一化されている。このため、中間貯蔵設備における粗粒土X6と細粒土X8の放射能レベルの測定及び管理が容易となる。   Furthermore, according to the soil continuous processing system 1 of this embodiment, in the slurry production | generation apparatus 5, the coarse grain soil X6 and the fine grain soil X8 which are contained in the slurry X5 are equalized. For this reason, it becomes easy to measure and manage the radioactivity levels of the coarse-grained soil X6 and the fine-grained soil X8 in the intermediate storage facility.

また、本実施形態の土壌連続処理システム1においては、沈降分離機6から排出される懸濁水X7を一時的に貯留して凝集分離装置11に供給する濁水槽9をさらに備える。このため、例えば、原土X1に含まれる放射性物質の濃度に変化が生じ、沈降分離機6から排出される懸濁水X7の放射性物質の濃度が急激に変化した場合であっても、濁水槽9より下流側には、濃度変化前の懸濁水X7と濃度変化後の懸濁水X7とが混合されて排出されるため、収容箱13に溜まる細粒土X8の濃度変化を緩やかにすることができる。よって、細粒土X8を収容する収容容器の濃度が急に変化することを抑止することができ、中間貯蔵設備における管理が容易となる。   The soil continuous treatment system 1 of the present embodiment further includes a muddy water tank 9 that temporarily stores the suspended water X7 discharged from the sedimentation separator 6 and supplies the suspended water X7 to the flocculation separation device 11. For this reason, for example, even if the concentration of the radioactive substance contained in the raw soil X1 changes and the concentration of the radioactive substance in the suspension water X7 discharged from the sedimentation separator 6 changes abruptly, the turbid water tank 9 Since the suspended water X7 before the concentration change and the suspended water X7 after the concentration change are mixed and discharged further downstream, the concentration change of the fine-grained soil X8 accumulated in the storage box 13 can be moderated. . Therefore, it can suppress that the density | concentration of the storage container which accommodates the fine-grained soil X8 changes suddenly, and management in an intermediate storage facility becomes easy.

また、本実施形態の土壌連続処理システム1においては、濁水槽9に貯留された懸濁水X7を攪拌する攪拌装置9bを備える。このため、懸濁水X7における放射性物質の濃度をより均一にすることができ、貯蔵単位ごとに分別土壌の放射能濃度を均一化することができる。   Moreover, in the soil continuous processing system 1 of this embodiment, the stirring apparatus 9b which stirs the suspension water X7 stored in the muddy water tank 9 is provided. For this reason, the density | concentration of the radioactive substance in suspension water X7 can be made more uniform, and the radioactivity density | concentration of fractionated soil can be equalized for every storage unit.

また、本実施形態の土壌連続処理システム1においては、濁水槽9の容量は、凝集分離装置11で分離された細粒土X8が詰められる収容容器の容量以上であるとされている。このため、細粒土X8を収容容器に詰めたときに、1つの収容容器に収容される放射性物質の濃度が大きく変化することを防止することができる。   Moreover, in the soil continuous processing system 1 of this embodiment, the capacity | capacitance of the muddy water tank 9 is supposed to be more than the capacity | capacitance of the storage container with which the fine-grained soil X8 isolate | separated with the aggregation separation apparatus 11 is packed. For this reason, when the fine-grained soil X8 is packed in the storage container, it is possible to prevent the concentration of the radioactive substance stored in one storage container from changing greatly.

以上、添付図面を参照しながら本発明の好適な実施形態について説明したが、本発明は、上記実施形態に限定されないことは言うまでもない。上述した実施形態において示した各構成部材の諸形状や組み合わせ等は一例であって、本発明の趣旨から逸脱しない範囲において設計要求等に基づき種々変更可能である。   As mentioned above, although preferred embodiment of this invention was described referring an accompanying drawing, it cannot be overemphasized that this invention is not limited to the said embodiment. Various shapes, combinations, and the like of the constituent members shown in the above-described embodiments are examples, and various modifications can be made based on design requirements and the like without departing from the spirit of the present invention.

例えば、上記実施形態においては、振動篩機2を用いて原土X1から分別土X2を分離する構成について説明した。しかしながら、本発明はこれに限定されるものではなく、他の装置を用いて原土X1から分別土X2を分離したり、振動篩機2を省略して作業者等によって予め分離された分別土X2を用いたりするようにしても良い。また、原土X1に可燃物X3や不燃物X4が含まれていないような場合には、原土X1を本発明の混合土として用い、振動篩機2を省略しても良い。   For example, in the said embodiment, the structure which isolate | separates the classification soil X2 from the raw soil X1 using the vibration sieve machine 2 was demonstrated. However, the present invention is not limited to this, and the separated soil X2 is separated from the raw soil X1 by using another device, or the separated soil previously separated by an operator or the like by omitting the vibration sieve 2. X2 may be used. Moreover, when the combustible material X3 and the incombustible material X4 are not contained in the raw soil X1, the raw soil X1 may be used as the mixed soil of the present invention, and the vibration sieve device 2 may be omitted.

1……土壌連続処理システム、2……振動篩機、3……第1ベルトコンベア、4……ホッパ、5……スラリー生成装置、6……沈降分離機、7……第1スクリューコンベア、8……第2ベルトコンベア、9……濁水槽、9a……貯留槽、9b……攪拌装置、10……濁水ポンプ、11……凝集分離装置、11a……凝集剤添加装置、11b……凝集反応管、11c……遠心分離脱水機、12……第2スクリューコンベア、13……コンクリートカルバートボックス、14……返送ポンプ、15……水槽、16……低圧ポンプ、17……高圧ポンプ、X1……原土、X2……分別土(混合土)、X3……可燃物、X4……不燃物、X5……スラリー、X6……粗粒土、X7……懸濁水、X8……細粒土、X9……水   DESCRIPTION OF SYMBOLS 1 ... Soil continuous processing system, 2 ... Vibrating sieve machine, 3 ... 1st belt conveyor, 4 ... Hopper, 5 ... Slurry production | generation apparatus, 6 ... Settling separator, 7 ... 1st screw conveyor, 8: Second belt conveyor, 9: Turbid water tank, 9a: Storage tank, 9b: Stirrer, 10: Turbid water pump, 11: Coagulation / separation apparatus, 11a: Coagulant addition apparatus, 11b ... Aggregation reaction tube, 11c: centrifugal dehydrator, 12: second screw conveyor, 13: concrete culvert box, 14: return pump, 15: water tank, 16: low pressure pump, 17: high pressure pump, X1 ... Rough soil, X2 ... Separated soil (mixed soil), X3 ... Combustible material, X4 ... Incombustible material, X5 ... Slurry, X6 ... Coarse-grained soil, X7 ... Suspended water, X8 ... Fine Grain soil, X9 ... water

Claims (4)

放射能レベルが低い粗粒土と放射能レベルが高くかつ前記粗粒土よりも粒径の小さい細粒土とを含む混合土を、噴射ノズルより噴射した水と混合してスラリーを生成するスラリー生成装置と、
前記スラリーを沈降分離により前記粗粒土と前記細粒土を含む懸濁水とに分離する沈降分離機と、
前記懸濁水に凝集剤を添加して前記細粒土を凝集させて分離する凝集分離装置と
を備えることを特徴とする土壌連続処理システム。
A slurry in which a mixed soil containing a coarse-grained soil having a low radioactivity level and a fine-grained soil having a high radioactivity level and a particle diameter smaller than that of the coarse-grained soil is mixed with water jetted from a jet nozzle to form a slurry. A generating device;
A sedimentation separator for separating the slurry into the coarse-grained soil and the suspended water containing the fine-grained soil by sedimentation;
A continuous soil treatment system, comprising: a flocculent separation device that adds a flocculant to the suspended water to clump and separate the fine-grained soil.
前記沈降分離機から排出される懸濁水を一時的に貯留して前記凝集分離装置に供給する濁水槽をさらに備えることを特徴とする請求項1記載の土壌連続処理システム。   The soil continuous treatment system according to claim 1, further comprising a muddy water tank for temporarily storing the suspended water discharged from the sedimentation separator and supplying the suspended water to the coagulation separator. 前記濁水槽に貯留された前記懸濁水を攪拌する攪拌装置を備えることを特徴とする請求項2記載の土壌連続処理システム。   The soil continuous processing system according to claim 2, further comprising a stirring device for stirring the suspension water stored in the muddy water tank. 前記濁水槽の容量は、前記凝集分離装置で分離された細粒土が詰められる収容容器の容量以上であることを特徴とする請求項2または3記載の土壌連続処理システム。   4. The soil continuous treatment system according to claim 2, wherein the capacity of the muddy water tank is equal to or greater than the capacity of a storage container filled with fine-grained soil separated by the coagulation / separation apparatus.
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JP2016043332A (en) * 2014-08-26 2016-04-04 株式会社安藤・間 Contaminated soil cleaning method and system
JP2016176716A (en) * 2015-03-18 2016-10-06 Jfeエンジニアリング株式会社 Apparatus and method for treating contaminated soil
JP2016200437A (en) * 2015-04-08 2016-12-01 株式会社東芝 Method for processing soil containing radioactive cesium

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JP2005137991A (en) * 2003-11-05 2005-06-02 Yasukura Sakai Drainage treatment apparatus
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JP2016043332A (en) * 2014-08-26 2016-04-04 株式会社安藤・間 Contaminated soil cleaning method and system
JP2016176716A (en) * 2015-03-18 2016-10-06 Jfeエンジニアリング株式会社 Apparatus and method for treating contaminated soil
JP2016200437A (en) * 2015-04-08 2016-12-01 株式会社東芝 Method for processing soil containing radioactive cesium

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