JP2002022893A - Method for making radioactive waste disposal facility low permeable - Google Patents
Method for making radioactive waste disposal facility low permeableInfo
- Publication number
- JP2002022893A JP2002022893A JP2000202416A JP2000202416A JP2002022893A JP 2002022893 A JP2002022893 A JP 2002022893A JP 2000202416 A JP2000202416 A JP 2000202416A JP 2000202416 A JP2000202416 A JP 2000202416A JP 2002022893 A JP2002022893 A JP 2002022893A
- Authority
- JP
- Japan
- Prior art keywords
- radioactive waste
- waste disposal
- concrete structure
- filler
- permeability
- 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.)
- Granted
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E30/00—Energy generation of nuclear origin
- Y02E30/30—Nuclear fission reactors
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/30—Landfill technologies aiming to mitigate methane emissions
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、放射性廃棄物処分
施設の低透水化方法に関する。The present invention relates to a method for reducing water permeability of a radioactive waste disposal facility.
【0002】[0002]
【従来の技術】廃棄物においては、その種類に応じて性
状が多岐に亘るため、その貯蔵方法も種々存在し、実用
化されている。このうち、放射性廃棄物の処分施設とし
て、中空円筒形の地下コンクリート構造物がある。この
内部に貯蔵する場合、廃棄物定置後に、廃棄物から発生
するガスを内部間隙から安全に透過させる高透気性と、
地下水の浸入を抑制できる低透水性が要求される材料を
充填し、速やかに固形化することが行われている。この
高透気性と低透水性のある材料として、無機系のポーラ
スモルタルなどが挙げられ、これらを充填することで、
ガス抜きを行いつつ放射性廃棄物を貯蔵する方法があ
る。2. Description of the Related Art Since wastes have various properties depending on their types, there are various methods of storing the wastes, and the wastes have been put into practical use. Among these, there is a hollow cylindrical underground concrete structure as a disposal facility for radioactive waste. When stored inside this, after the waste is placed in place, high air permeability that allows gas generated from the waste to safely pass through the internal gap,
2. Description of the Related Art Materials that require low water permeability that can suppress infiltration of groundwater are filled and quickly solidified. As the material having high air permeability and low water permeability, inorganic porous mortar and the like are mentioned, and by filling these,
There is a method of storing radioactive waste while degassing.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、この方
法では、施工時に充填材に急速な水和熱が発生し、剛性
の高いセメント系充填材が熱膨張し、コンクリート構造
物に内圧が作用し、引張応力が発生して、ひび割れの要
因となる。また、廃棄物から発生するガスの圧力も構造
物に内圧として作用し、同じく引張応力が発生し、ひび
割れの原因となる。これにより、地下水が存在する場合
には、ひび割れを伝って構造物内部に侵入し、水漏れの
原因となるといった課題がある。However, according to this method, a rapid heat of hydration is generated in the filler at the time of construction, the rigid cement-based filler thermally expands, and the internal pressure acts on the concrete structure. Tensile stress is generated, which causes cracking. In addition, the pressure of the gas generated from the waste also acts as an internal pressure on the structure, which also generates a tensile stress and causes cracks. As a result, when groundwater is present, there is a problem that it penetrates into the structure through cracks and causes water leakage.
【0004】本発明は、以上の課題を解決するものであ
って、その目的は、コンクリート構造物に発生する引張
応力を抑制することで、コンクリート構造物の低透水性
を維持できるようにした放射性廃棄物処分施設の低透水
化方法を提供するものである。An object of the present invention is to solve the above-mentioned problems, and an object of the present invention is to suppress the tensile stress generated in a concrete structure so that a radioactive material capable of maintaining a low water permeability of the concrete structure can be maintained. It is intended to provide a method for reducing water permeability of a waste disposal facility.
【0005】[0005]
【課題を解決するための手段】以上の目的を達成するた
め、本発明方法は、閉断面を有する地下コンクリート構
造物の内部空間に複数の放射性廃棄物を定置した後、該
廃棄物の間隙に高透気性及び低透水性のあるセメント系
充填材を充填して一体的に固化させるようにした放射性
廃棄物処分施設において、前記充填材に対する初期加水
量を0ないし必要最小限とし、施設閉鎖後の地下水の浸
透に応じて徐々に水和反応を生じさせることを特徴とす
るものである。従って、本発明方法では、水和反応が緩
慢であり、大きな発熱を生ずることがなく、熱応力によ
り、構造物に温度ひび割れなどの不具合が発生するのを
防止できる。In order to achieve the above object, the method of the present invention comprises: placing a plurality of radioactive wastes in an internal space of an underground concrete structure having a closed section; In a radioactive waste disposal facility that is filled with a highly air-permeable and low-water-permeability cement-based filler and solidified integrally, the initial amount of water added to the filler is reduced to 0 or a necessary minimum. The hydration reaction is caused gradually according to the infiltration of groundwater. Therefore, in the method of the present invention, the hydration reaction is slow, large heat generation does not occur, and it is possible to prevent the occurrence of problems such as temperature cracks in the structure due to thermal stress.
【0006】本発明方法はまた、閉断面を有する地下コ
ンクリート構造物の内部空間に複数の放射性廃棄物を定
置した後、該廃棄物の間隙に高透気性及び低透水性のあ
るセメント系充填材を充填して一体的に固化させるよう
にした放射性廃棄物処分施設において、前記コンクリー
ト構造物の内面に鋼材などからなる突起材を予め突出さ
せ、前記充填材と一体化させることを特徴とするもので
ある。従って、本発明方法では、充填材が収縮すること
で突起物を内部に引っ張り、コンクリート構造物を全体
として圧縮するので、内部に向けたプレストレスが導入
される結果、ガス圧により発生する引張応力を抑制する
ことができる。[0006] The method of the present invention also includes a method of placing a plurality of radioactive wastes in an internal space of an underground concrete structure having a closed cross section, and then filling a gap between the wastes with a cement-based filler having high air permeability and low water permeability. In a radioactive waste disposal facility that is filled and solidified integrally, a projection made of steel or the like is projected in advance on the inner surface of the concrete structure, and is integrated with the filler. It is. Therefore, in the method of the present invention, since the protrusions are pulled inward by the shrinkage of the filler and the concrete structure is compressed as a whole, a prestress directed toward the inside is introduced, so that the tensile stress generated by the gas pressure is generated. Can be suppressed.
【0007】[0007]
【発明の実施の形態】以下、本発明の好ましい実施の形
態につき、添付図面を参照して詳細に説明する。図1
は、本発明方法を適用した廃棄物処分施設を示すもの
で、周囲岩盤E内に構築された中空円筒形の地下コンク
リート構造物1からなっており、この構造物1の内部
に、例えば立方体に固形化された多数の放射性廃棄物2
を縦横マトリックス状に定置し、各廃棄物2の隙間に充
填材3を充填する作業を下部から順に繰返すことで構造
物1の内部が満たされることにより、施設が閉鎖され
る。Preferred embodiments of the present invention will be described below in detail with reference to the accompanying drawings. Figure 1
Indicates a waste disposal facility to which the method of the present invention is applied, and is composed of a hollow cylindrical underground concrete structure 1 built in a surrounding rock E, and inside the structure 1, for example, a cube Many solidified radioactive wastes 2
Are arranged in the form of a matrix, and the operation of filling the gaps between the wastes 2 with the filler 3 is repeated in order from the bottom to fill the inside of the structure 1, thereby closing the facility.
【0008】充填材3としては、例えばポーラスコンク
リートのごとく、高透気性と低透水性のあるセメント系
充填材が用いられる。加えて本発明方法では、従来と比
べて、充填材3に混和される水量は全量がただちに水和
反応を生じないような水:セメント比で混練された材
料、あるいはモルタル成分の乾燥粉体のまま充填する作
業が満杯になるまで繰り返される。As the filler 3, a cement-based filler having high air permeability and low water permeability, such as porous concrete, is used. In addition, in the method of the present invention, the amount of water to be mixed with the filler 3 is smaller than that of the conventional method in that a water: cement ratio of a material kneaded or a dry powder of a mortar component is such that the hydration reaction does not immediately occur. The operation of filling as it is is repeated until it is full.
【0009】以上の方法における初期状態においては、
図2(a)に示すように、廃棄物2の発熱により内部が
膨張しても(内部膨張圧を矢印図示)、充填材3は未だ
十分に硬化しておらず、従ってその外周のコンクリート
構造物1に有害な内圧は生じない。また、岩盤E内の地
下水圧がコンクリート構造物1に作用する時には(地下
水圧を矢印図示)、充填材3までに浸潤していないた
め、廃棄物貯蔵部は低剛性であり、図2(b)に示すよ
うに、圧縮応力が導入される。In the initial state in the above method,
As shown in FIG. 2 (a), even if the interior expands due to the heat generated by the waste 2 (the internal expansion pressure is indicated by an arrow), the filler 3 has not been sufficiently hardened yet, and accordingly, the concrete structure on the outer periphery thereof No harmful internal pressure is generated in the object 1. Further, when the groundwater pressure in the bedrock E acts on the concrete structure 1 (groundwater pressure is indicated by an arrow), the waste storage portion has low rigidity because it does not infiltrate to the filler 3. ), A compressive stress is introduced.
【0010】この状態から経時変化により、構造物1の
内部に地下水が内部に順次浸透すると(透水状況を矢印
図示)、図2(c)に示すように、周囲から順次充填材
3の緩慢な水和反応が生ずる。この際の発熱量は従来に
比べて極めて少なく、加えて水和収縮により、構造物に
は内側に向けたプレストレスが導入され、ひび割れを発
生しにくくする。[0010] From this state, as the groundwater sequentially permeates into the structure 1 due to a change with time (illustration of the permeation state is indicated by an arrow), as shown in FIG. A hydration reaction occurs. At this time, the calorific value is extremely small as compared with the related art, and in addition, due to hydration shrinkage, a prestress directed inward is introduced into the structure, thereby making it difficult to generate cracks.
【0011】なお、構造物1の内側に予め鋼材などの突
起材(図示しない)を適宜間隔をおいて複数突出形成し
ておくことにより(法線方向に突出することが好まし
い)、充填材3の硬化にともない、突起材を内側に向け
て引っ張り込む力が作用し、構造物1に内側に向くプレ
ストレスが導入されることになる結果、ガス圧により発
生する内圧を抑制することができる。By forming a plurality of projecting members (not shown) such as steel materials in advance inside the structure 1 at appropriate intervals (preferably projecting in the normal direction), the filling material 3 is formed. With the hardening of the material, a force for pulling the protruding material toward the inside acts, and prestress toward the inside is introduced into the structure 1, so that the internal pressure generated by the gas pressure can be suppressed.
【0012】また、構造物1を透過した微小な透水は、
充填材3を通過する過程で水和反応に消費され、さらに
は図2(c)の一部に拡大して示すように、コンクリー
ト打設時に発生した気泡や、水和減量により生じた空隙
内3aに保水されることから、さらに中心側には透水し
がたいものとなる。Further, the minute water permeation that has passed through the structure 1 is as follows:
In the process of passing through the filler 3, it is consumed by the hydration reaction, and further as shown in an enlarged part of FIG. Since the water is retained at 3a, it is difficult for the center to permeate.
【0013】以上のような地下水の浸潤に伴う充填材の
極めて緩慢な水和反応を伴う硬化が完了した後は、高剛
性となり、外圧による構造物1の収縮変形が抑制され、
ひび割れが発生し難いものとなる。また、その逆に廃棄
物2から発生するガスの圧力による引張応力を抑制する
ものとなるといった優れた効果を奏する。After the above-mentioned hardening accompanied by the extremely slow hydration reaction of the filler due to the infiltration of the groundwater is completed, the filler becomes highly rigid, and the contraction deformation of the structure 1 due to the external pressure is suppressed,
Cracks hardly occur. On the contrary, there is an excellent effect that the tensile stress due to the pressure of the gas generated from the waste 2 is suppressed.
【0014】[0014]
【発明の効果】以上の説明により明らかなように、本発
明による放射性廃棄物処分施設の低透水化方法にあって
は、外圧を導入し、かつ内圧を抑制することにより、止
水欠陥の発生を抑え、コンクリート構造物の低透水性を
維持する。As is apparent from the above description, in the method for reducing water permeability of a radioactive waste disposal facility according to the present invention, the occurrence of water stoppage defects is achieved by introducing external pressure and suppressing internal pressure. And maintain low water permeability of concrete structures.
【図1】本発明方法を適用した放射性廃棄物処分施設の
平断面図である。FIG. 1 is a plan sectional view of a radioactive waste disposal facility to which the method of the present invention is applied.
【図2】(a)〜(c)は同方法における経時変化を示
す説明用平面図である。FIGS. 2 (a) to 2 (c) are explanatory plan views showing temporal changes in the same method.
1 地下コンクリート構造物 2 放射性廃棄物 3 セメント系充填材 1 Underground concrete structure 2 Radioactive waste 3 Cement-based filler
Claims (2)
の内部空間に複数の放射性廃棄物を定置した後、該廃棄
物の間隙に高透気性及び低透水性のあるセメント系充填
材を充填して一体的に固化させるようにした放射性廃棄
物処分施設において、 前記充填材に対する初期加水量を0ないし必要最小限と
し、施設閉鎖後の地下水の浸透に応じて徐々に水和反応
を生じさせることを特徴とする放射性廃棄物処分施設の
低透水化方法。After a plurality of radioactive wastes are set in an internal space of an underground concrete structure having a closed section, a gap between the wastes is filled with a cement filler having high air permeability and low water permeability. In a radioactive waste disposal facility that is solidified integrally, the initial amount of water added to the filler is reduced to 0 or a necessary minimum, and a hydration reaction is gradually generated according to the infiltration of groundwater after the facility is closed. Characteristic low-permeability method for radioactive waste disposal facilities.
の内部空間に複数の放射性廃棄物を定置した後、該廃棄
物の間隙に高透気性及び低透水性のあるセメント系充填
材を充填して一体的に固化させるようにした放射性廃棄
物処分施設において、 前記コンクリート構造物の内面に鋼材などからなる突起
材を予め突出させ、前記充填材と一体化させることを特
徴とする放射性廃棄物処分施設の低透水化方法。2. After placing a plurality of radioactive wastes in the interior space of an underground concrete structure having a closed cross section, filling the gaps between the wastes with a cement filler having high air permeability and low water permeability. In a radioactive waste disposal facility that is solidified integrally, a radioactive waste disposal facility characterized in that a protrusion made of steel or the like is projected in advance on the inner surface of the concrete structure and integrated with the filler. Low water permeability method.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000202416A JP3918408B2 (en) | 2000-07-04 | 2000-07-04 | Low water permeability method for radioactive waste disposal facility, radioactive waste disposal facility |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000202416A JP3918408B2 (en) | 2000-07-04 | 2000-07-04 | Low water permeability method for radioactive waste disposal facility, radioactive waste disposal facility |
Related Child Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2006187462A Division JP3933187B2 (en) | 2006-07-07 | 2006-07-07 | Low water permeability method for radioactive waste disposal facility, radioactive waste disposal facility |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2002022893A true JP2002022893A (en) | 2002-01-23 |
JP3918408B2 JP3918408B2 (en) | 2007-05-23 |
Family
ID=18699944
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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JP2000202416A Expired - Fee Related JP3918408B2 (en) | 2000-07-04 | 2000-07-04 | Low water permeability method for radioactive waste disposal facility, radioactive waste disposal facility |
Country Status (1)
Country | Link |
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JP (1) | JP3918408B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008100154A (en) * | 2006-10-18 | 2008-05-01 | Shimizu Corp | Gas-permeable passage member for reclamation facility and reclamation facility |
-
2000
- 2000-07-04 JP JP2000202416A patent/JP3918408B2/en not_active Expired - Fee Related
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008100154A (en) * | 2006-10-18 | 2008-05-01 | Shimizu Corp | Gas-permeable passage member for reclamation facility and reclamation facility |
Also Published As
Publication number | Publication date |
---|---|
JP3918408B2 (en) | 2007-05-23 |
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