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JP2015102359A - Radioactive waste underground storage facility and construction method thereof - Google Patents

Radioactive waste underground storage facility and construction method thereof Download PDF

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JP2015102359A
JP2015102359A JP2013241443A JP2013241443A JP2015102359A JP 2015102359 A JP2015102359 A JP 2015102359A JP 2013241443 A JP2013241443 A JP 2013241443A JP 2013241443 A JP2013241443 A JP 2013241443A JP 2015102359 A JP2015102359 A JP 2015102359A
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disposal
water
radioactive waste
storage facility
underground storage
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JP5740456B2 (en
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孝義 大塚
Takayoshi Otsuka
孝義 大塚
小林 亨
Toru Kobayashi
亨 小林
亨 神田
Toru Kanda
亨 神田
則行 菅原
Noriyuki Sugawara
則行 菅原
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I TOP CO Ltd
Nippon Civic Consulting Engineers Co Ltd
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Nippon Civic Consulting Engineers Co Ltd
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Abstract

PROBLEM TO BE SOLVED: To provide an underground storage facility having a large disposal space for efficiently performing burial disposal (geological disposal/marginal depth disposal) of radioactive waste.SOLUTION: In a method, vertical shafts 1 are formed down to a predetermined depth, each of which has a diameter enough to locate and drive a drilling unit 3 for constructing disposal tunnels 2 by using a shield method, and the disposal tunnels 2 are constructed from the respective vertical shafts by using the shield method of machine-drilling and assembling concrete segments. The disposal tunnel 2 is constructed to form a disposal space having a perfect water-shielding structure which includes: a primary lining having a water-shielding structure formed by attaching sealing materials in advance around the entire periphery of end surfaces of the segments used in the shield method; a continuous water-shielding layer formed by heat welding water-shielding sheets on the inner wall surface of the primary lining; and a secondary lining with concrete inside the water-shielding layer.

Description

本発明は、放射性廃棄物の地下貯蔵施設およびその構築方法に関するものである。   The present invention relates to a radioactive waste underground storage facility and a construction method thereof.

原子力発電所や再処理施設からでる放射性廃棄物は、高レベル放射性廃棄物と低レベル放射性廃棄物に区分され、高レベル放射性廃棄物は、廃棄処理される使用済燃料そのもの、及び使用済燃料を再処理してウラン・プルトニウムを回収後に残る核分裂生成物を主成分とするものである。この高レベル放射性廃棄物の処理は、現在ホウケイ酸ガラスと混合溶融してステンレス製容器(キャニスタ)に注入して固化させ、廃棄体として貯蔵する。この貯蔵手段は、一定期間冷却貯蔵した後、地下深部(地上から300m以上の深さ)に埋設貯蔵する地層処分が法で定められている。   Radioactive waste from nuclear power plants and reprocessing facilities is divided into high-level radioactive waste and low-level radioactive waste, and high-level radioactive waste is used as spent fuel itself to be disposed of as well as spent fuel. It consists mainly of fission products that remain after recovery and recovery of uranium and plutonium. This high-level radioactive waste is currently mixed and melted with borosilicate glass, poured into a stainless steel container (canister), solidified, and stored as waste. This storage means that the geological disposal to store in the deep underground (depth of 300m or more from the ground) after cooling and storing for a certain period is stipulated by law.

また低レベル放射性廃棄物の内、原子炉内の構造物や、使用済み制御棒のような放射能レベルが比較的高い廃棄物は、所定の容器に封入して廃棄体とし、余裕深度処分(50〜100mの埋設処分)を行う。   Among the low-level radioactive waste, wastes with relatively high levels of radioactivity, such as reactor structures and used control rods, are sealed in a predetermined container to form a waste body, which can be disposed at a sufficient depth ( 50-100m buried disposal).

地層処分施設となる地下貯蔵施設の代表的な例は、特許文献1,2に示されている。この施設は、廃棄体(キャニスタ)を地下に搬入する立抗と、立坑と連続する多数の貯蔵用横坑道を備え、各横坑道(処分坑道)の底面に、下方へ掘削した処分孔を間欠的に形成し、各処分孔に人工バリア材(ベントナイト等)で覆った状態で廃棄体を埋設処分するものである。また、低レベル放射性廃棄物の埋設処分手段の例として特許文献3に、岩盤内に形成した処分坑道を処分空間とし、廃棄物を多段積層し、周囲を低拡散物で充填する構成が開示されている。   The typical example of the underground storage facility used as the geological disposal facility is shown in Patent Documents 1 and 2. This facility is equipped with a stand to carry waste (canister) underground, and a large number of storage horizontal tunnels connected to the vertical shaft. Disposal holes drilled downward are intermittently formed on the bottom of each horizontal tunnel (disposal tunnel). The waste is buried and disposed in a state in which each disposal hole is covered with an artificial barrier material (such as bentonite). In addition, as an example of a low-level radioactive waste embedding disposal means, Patent Document 3 discloses a configuration in which a disposal tunnel formed in the rock is used as a disposal space, waste is multi-layered, and the surroundings are filled with low-diffusion materials. ing.

尚前記の特許文献1には、また処分坑道の構造として、鋼製枠に花崗岩を充填したセグメントで支保構造を形成することが開示されている。   In addition, the above-mentioned patent document 1 discloses that a supporting structure is formed by a segment in which a steel frame is filled with granite as a structure of a disposal tunnel.

更に地下貯蔵施設において、貯蔵される廃棄体等からの汚染物質が、地下水への浸透を阻止する手段として、特許文献2には、従来例として健全岩盤間に存在する断層破砕帯を貫通する処分坑道に粘土材料による止水プラグを構築することが示されており、その対策として断層破砕帯を避けて処分坑道を岩盤内に構築することが提案されている。   Furthermore, in the underground storage facility, as a means for preventing contaminants from stored waste and the like from penetrating into the groundwater, Patent Document 2 discloses disposal through a fault crushing zone existing between healthy rocks as a conventional example. It has been shown that a water stop plug made of clay material is constructed in a mine shaft, and as a countermeasure against this, it is proposed to construct a disposal mine shaft in the rock mass while avoiding a fault fracture zone.

また特許文献3には、常法手段で構築したコンクリート覆工で形成した処分坑道の内壁面に、ベントナイトブロックを配置して抵透水層を設け、更に前記低透水層の内側に鉄筋コンクリート製セグメントを配置して、処分空間を構築する工法が開示されている。   Further, Patent Document 3 discloses that a bentonite block is disposed on an inner wall surface of a disposal mine formed by a concrete lining constructed by a conventional method to provide a water permeable layer, and a reinforced concrete segment is provided inside the low water permeable layer. A method for arranging and constructing a disposal space is disclosed.

特開2002−250795号公報。JP 2002-250795 A. 特開2005−331313号公報。JP-A-2005-331313. 特開2004−298822号公報。JP 2004-298822 A.

高レベル放射性廃棄物は、所定の廃棄体として地層処分されるが、従前の地下貯蔵施設の処分坑道は、岩盤層での形成を前提としており、更に処分坑道から下方に処分孔を掘削しての埋設処理を行うもので多数の処分坑道並びに処分孔を掘削する必要があり、施設構築が必ずしも効率的であるとは言えない。   High-level radioactive waste is geologically disposed as a predetermined waste body, but the disposal tunnel of the previous underground storage facility is premised on the formation of the rock layer, and further, a disposal hole is drilled downward from the disposal tunnel. It is necessary to excavate many disposal tunnels and disposal holes, and it cannot be said that the construction of facilities is necessarily efficient.

また処分坑道や、廃棄体保管のための遮水構造として、ベントナイト系のブロックによるトンネル壁面の形成や、廃棄体の周囲を充填物で満たす手段が提案されているが、遮水用構造物の体積の比率が大きくなり処分空間の利用率が良好とは言えない。   Also, as a water-blocking structure for disposal tunnels and waste storage, tunnel wall formation with bentonite blocks and means for filling the surroundings with waste have been proposed. The volume ratio becomes large, and the utilization rate of the disposal space is not good.

そこで本発明は、放射性廃棄物の埋設処分(地層処分・余裕深度処分)が効率的に行うことができる新規な放射性廃棄物の地下貯蔵施設およびその構築方法を提案したものである。   Therefore, the present invention proposes a novel radioactive waste underground storage facility and a method for constructing it, which can efficiently carry out the disposal of radioactive waste (geological disposal and marginal depth disposal).

本発明の請求項1に係る放射性廃棄物の地下貯蔵施設は、施設構築エリア内で、所定の掘削装置が配置可能な径の立坑と、前記立坑から適宜方向に適宜数本を枝設すると共に、端面全周に止水シール材を装着したコンクリートセグメントによる遮水構造の一次覆工、及び前記一次覆工の内壁面に遮水シートで形成した遮水層、及び前記遮水層の内側のコンクリートによる二次覆工によって三重の完全遮水構造とした処分空間を備える処分坑道とで構成することを特徴とするものである。
とするものである。
In the underground storage facility for radioactive waste according to claim 1 of the present invention, a shaft having a diameter in which a predetermined excavation device can be arranged and a plurality of appropriate branches from the shaft in an appropriate direction are provided in the facility construction area. A primary lining of a water-blocking structure with a concrete segment fitted with a water-stop sealant around the entire end surface, a water-blocking layer formed of a water-blocking sheet on the inner wall surface of the primary lining, and an inner side of the water-blocking layer It is characterized by comprising a disposal tunnel with a disposal space that has a triple water-tight structure by secondary lining with concrete.
It is what.

また本発明の請求項5に係る放射性廃棄物の地下貯蔵施設の構築方法は、施設構築エリア内で、所定の掘削装置が配置可能な径の立坑を所定の深さまで形成し、前記立坑からマシン掘削とコンクリートセグメントの組立によるシールド工法で処分坑道を構築する際に、前記セグメントの端面全周に予め止水シール材を装着して遮水構造の一次覆工を行い、前記一次覆工の内壁面に、熱溶着によって連続する遮水シートによる遮水層を形成し、前記遮水層の内側にコンクリートによる二次覆工を行って、三重の完全遮水構造の処分空間を形成してなることを特徴とするものである。   According to a fifth aspect of the present invention, there is provided a method for constructing an underground storage facility for radioactive waste, wherein a shaft having a diameter on which a predetermined excavator can be disposed is formed to a predetermined depth in a facility construction area, and a machine is formed from the shaft. When constructing a disposal tunnel by shield method by excavation and assembly of concrete segments, a water-blocking seal is preliminarily attached to the entire periphery of the end face of the segment to perform primary lining of the water-blocking structure. Forming a water-impervious layer with a continuous water-impervious sheet by thermal welding on the wall surface, and performing secondary lining with concrete inside the water-impervious layer to form a disposal space with a triple completely impermeable structure It is characterized by this.

而して埋設処分対象が、高レベル放射性廃棄物の廃棄体の地層処分か、或いは放射能レベルが比較的高い低レベル放射性廃棄物の廃棄体の余裕深度処分かによって立坑の掘削深度が定められる。またその立坑の掘削径は、処分坑道の掘削に採用されるシールド工法に使用する掘削装置(密閉タイプ、開放タイプ、密閉・開放切替タイプなど、地層状態に応じて採用される)を、立坑の底方に配置して発進可能となる大きさとし、前記の立坑掘削後に、当該立坑から前記掘削装置で処分坑道を掘削形成するものである。更に前記の処分坑道は、掘削方向や掘削高さを相違させることによって複数本形成することができ、当該施設構築エリア内での広い処分空間を容易に確保できるものである。而も前記の法処分坑道は一次覆工、遮水層、二次覆工によって処分坑道内の全体が、地下水汚染を防止した三重の完全遮水構造の処分空間となる。また前記立坑は廃棄体の搬入路となる。   Thus, the excavation depth of the shaft is determined depending on whether the disposal target is geological disposal of high-level radioactive waste waste or low-level radioactive waste waste with relatively high radioactivity level. . In addition, the diameter of the shaft is the same as that used for the shield method used for excavation of disposal tunnels (sealed type, open type, sealed / open switching type, etc.). The size is such that it can be placed at the bottom and can be started, and after the shaft excavation, a disposal tunnel is excavated from the shaft with the excavator. Furthermore, a plurality of the disposal tunnels can be formed by making the excavation direction and the excavation height different, and a wide disposal space in the facility construction area can be easily secured. However, the above-mentioned legal disposal tunnel is a disposal space with a triple completely impermeable structure in which the entire disposal tunnel is prevented by the primary lining, the shielding layer, and the secondary lining. The vertical shaft is a waste carrying-in route.

本発明の請求項2及び6に係る放射性廃棄物の地下貯蔵施設及びその構築方法は、特に前記の地下貯蔵施設及びその構築方法において、施設構築エリア内で適宜な距離を離して構築した複数の立坑を形成し、前記各立坑間を結ぶように設けた処分坑道を形成してなるもので、当該施設構築エリアの範囲で地形や地盤条件に合わせて立坑位置を設定し、その間を結ぶ複数の処分坑道を構築することで、複数の処分坑道の同時施工が容易に可能であり、広い処分空間の構築を効率よく行うことができる。   The underground storage facility for radioactive waste and the construction method thereof according to claims 2 and 6 of the present invention, particularly in the underground storage facility and construction method thereof, are a plurality of constructions separated at an appropriate distance in the facility construction area. Forming shafts and forming disposal tunnels that are connected to connect the shafts. Set the shaft position according to the terrain and ground conditions within the facility construction area, and connect multiple shafts between them. By constructing a disposal tunnel, simultaneous construction of a plurality of disposal tunnels can be easily performed, and a wide disposal space can be efficiently constructed.

更に本発明の請求項3、7に係る放射性廃棄物の地下貯蔵施設及びその構築方法は、特に前記の地下貯蔵施設及びその構築方法において、特に立坑直径を約40m程度、処分坑道直径を16m程度とし、処分坑道内を多階層構造としたもので、放射性廃棄物の搬入等の廃棄体格納作業の全自動化を、階層毎に行うことが可能であり、効率的な格納作業を実現することができる。   Further, the radioactive waste underground storage facility and the construction method thereof according to claims 3 and 7 of the present invention, particularly in the underground storage facility and construction method thereof, are particularly about 40 m in diameter of the shaft and about 16 m in diameter of the disposal tunnel. The disposal tunnel has a multi-layered structure, and it is possible to perform full automation of waste storage work, such as carrying in radioactive waste, for each level, realizing efficient storage work. it can.

また本発明の請求項4に係る放射性廃棄物の地下貯蔵施設は、前記の処分坑道に多階層構造を採用した際に、特に処分坑道の各階に、適宜な緩衝材で所定の厚さに形成した貯蔵床面に、高レベル放射性廃棄体用の処分孔を形成してなるもので、高レベル放射性廃棄体の大量地層処分を実現できる。   Further, the radioactive waste underground storage facility according to claim 4 of the present invention is formed to have a predetermined thickness with an appropriate cushioning material on each floor of the disposal tunnel, particularly when a multi-level structure is adopted for the disposal tunnel. A disposal hole for high-level radioactive waste is formed on the storage floor, and a large-scale geological disposal of high-level radioactive waste can be realized.

また本発明の請求項8に係る放射性廃棄物の地下貯蔵施設の構築方法は、一次覆工におけるセグメントの内壁面に、セメント結晶増殖剤を塗布して緻密化処理を施してなるもので、一次覆工の堅牢性及び防水性を高める。   Moreover, the construction method of the underground storage facility of the radioactive waste according to claim 8 of the present invention is a method in which a cement crystal growth agent is applied to the inner wall surface of the segment in the primary lining and densification treatment is performed. Increases the robustness and waterproofness of the lining.

本発明の構成は上記のとおりで、放射性廃棄物の埋設処分のための大容量の地下処分空間を容易に構築することができるものである。   The configuration of the present invention is as described above, and a large-capacity underground disposal space for burying radioactive waste can be easily constructed.

本発明の実施形態の地下貯蔵施設の全体説明図。The whole explanatory view of the underground storage facility of the embodiment of the present invention. 同要部説明図。FIG. 同処分坑道に使用するセグメントの斜視図。The perspective view of the segment used for the disposal tunnel. 同処分坑道の断面図。Sectional drawing of the disposal tunnel. 同a−a線断面図。The aa sectional view taken on the line. 同貯蔵例の説明図。Explanatory drawing of the storage example.

次に本発明の実施形態(構築方法)をその工程順に説明する。実施形態に示した放射性廃棄物の地下貯蔵施設の構築は、所定の施設構築エリア内に構築されるもの、当該構築エリアの地形や地盤条件に合わせて、立坑間隔が数百から2km程度の範囲内で立坑位置を設定し、複数の立坑1を掘削形成する。   Next, an embodiment (construction method) of the present invention will be described in the order of the steps. The construction of the underground storage facility for radioactive waste shown in the embodiment is constructed in a predetermined facility construction area, and the vertical interval is about several hundred to 2 km according to the topography and ground conditions of the construction area. A shaft position is set in the inside, and a plurality of shafts 1 are formed by excavation.

立坑1は、埋設処分対象が、高レベル放射性廃棄物の廃棄体の地層処分か、或いは放射能レベルが比較的高い低レベル放射性廃棄物の廃棄体の余裕深度処分によって立坑の掘削深度が定められもので、前者の場合は通常300m以上の深さとし、後者の場合には50〜100mの深さとする。   As for the shaft 1, the excavation depth of the shaft is determined by the geological disposal of the waste of high-level radioactive waste or the marginal depth disposal of the waste of low-level radioactive waste having a relatively high radioactivity level. In the former case, the depth is usually 300 m or more, and in the latter case, the depth is 50 to 100 m.

また立坑1の直径は、約40m程度とし、処分坑道2の掘削を行う掘削装置3が立坑底に配置でき、且つ発進可能となる大きさとしたものである。   Moreover, the diameter of the shaft 1 is about 40 m, and the excavator 3 for excavating the disposal tunnel 2 can be disposed on the shaft bottom and can be started.

立坑1の構築が終了すると、掘削径16m程度の処分坑道2の構築を行うもので、坑道掘削は、掘削装置3と一次覆工に用いるセグメント21の組み合わせからなる周知のシールド工法を採用し、掘削装置3は、密閉タイプ、開放タイプ、密閉・開放切替タイプなど、地層状態に応じて選択される。   When the construction of the shaft 1 is completed, the disposal tunnel 2 having a drilling diameter of about 16 m is constructed. The tunnel excavation employs a well-known shield method composed of a combination of the excavator 3 and the segment 21 used for the primary lining, The excavator 3 is selected according to the formation state, such as a sealed type, an open type, and a closed / open switching type.

処分坑道2のトンネル形成に使用されるセグメント21は、コンクリートセグメントであり、特にセグメント21には、イモ継ぎするためのセグメント継手211、トンネル方向の連結手段であるトランスミッションストリップ212及びホゾ213を備えている他、端面全周に内外方二重のシール材214を装着してなる。尚前記シール材214はセグメント本体21に喰い込むアンカー部を備えた高性能アンカータイプのものである。またセグメント21のトンネル内面側には、セメント結晶増殖剤を塗布して緻密化処理を施しておき、後述する一次覆工における遮水性能を高めるものである。   The segment 21 used for the tunnel formation of the disposal mine tunnel 2 is a concrete segment, and in particular, the segment 21 includes a segment joint 211 for potato splicing, a transmission strip 212 that is a connecting means in the tunnel direction, and a HOZO 213. In addition, the inner and outer double sealing material 214 is mounted on the entire periphery of the end surface. The sealing material 214 is of a high-performance anchor type having an anchor portion that bites into the segment body 21. Further, a cement crystal growth agent is applied on the inner surface side of the tunnel of the segment 21 and subjected to a densification treatment, thereby improving the water shielding performance in the primary lining described later.

而して立坑1から掘削装置3で、岩盤Aに対して横方向(必ずしも水平に限られない)に他方の立坑1に向かって公知のシールド工法によって掘削を行うものである。   Thus, excavation is performed from the vertical shaft 1 to the other vertical shaft 1 by a known shield method in the lateral direction (not necessarily horizontal) with respect to the rock A.

即ち掘削装置3の前進に伴ってセグメント21をイモ継ぎで組み立てて、覆工するものである。特にセグメント21による覆工は、一次覆工とし、セグメント21による一次覆工の内壁面に、遮水層22を形成する。この遮水層22は、高密度ポリエチレンシート製の遮水シートを熱溶着で連続させて形成する。更に遮水層22の内壁面にコンクリートによる二次覆工23を施す。この三重の完全遮水構造によって地下水汚染を生じさせない処分空間(処分坑道)の地下構築を実現するものである。   That is, as the excavator 3 moves forward, the segment 21 is assembled with the potato joint and lining is performed. In particular, the lining by the segment 21 is a primary lining, and the water shielding layer 22 is formed on the inner wall surface of the primary lining by the segment 21. The water shielding layer 22 is formed by continuously forming a water shielding sheet made of a high density polyethylene sheet by thermal welding. Further, a secondary lining 23 made of concrete is applied to the inner wall surface of the water shielding layer 22. This triple complete water-blocking structure realizes underground construction of disposal space (disposal tunnel) that does not cause groundwater contamination.

前記の二次覆工23を終えた処分坑道2は、岩盤A、裏込め材B、二重シール材214で遮水構造に組み立てられた緻密化処理したセグメント21による一次覆工、遮水シートによる遮水層22、二次覆工23の三重遮水断面構造を備えることによって、処分坑道2内は、完全遮水構造とした処分空間24となるものである。この完全遮水構造の処分坑道2は、各立坑1間を接続する多数が構築され、所定の施設構築エリアの範囲で地形や地盤条件に合わせて構築される広い処分空間を備えた放射性廃棄物(廃棄体C)の地下貯蔵施設の全体の基本構造が出来上がるものである。   After the secondary lining 23 is completed, the disposal mine 2 is a primary lining by a densified segment 21 assembled into a water-blocking structure with a rock mass A, a backfill material B, and a double seal material 214, and a water-blocking sheet By providing the triple water-impervious cross-sectional structure of the water-impervious layer 22 and the secondary lining 23, the disposal tunnel 2 becomes a disposal space 24 having a completely impermeable structure. This completely impermeable disposal tunnel 2 is constructed with a large number of connections between the vertical shafts 1, and is a radioactive waste with a wide disposal space that is constructed according to the topography and ground conditions within the range of a predetermined facility construction area The entire basic structure of the underground storage facility of (Waste Body C) is completed.

前記の複数の立坑1及び処分坑道2を具体的な貯蔵施設とするには、処分坑道2の直径が16m程度の大口径であるので、効率的な廃棄体貯蔵を行うために、処分坑道2内にコンクリート床面25及び支柱26を建設し、処分坑道2の内部を多階層構造(例えば3階構造)とするものである。   In order to make the plurality of vertical shafts 1 and disposal tunnels 2 concrete storage facilities, the disposal tunnel 2 has a large diameter of about 16 m. Therefore, in order to efficiently store waste, the disposal tunnel 2 The concrete floor 25 and the column 26 are built inside, and the inside of the disposal tunnel 2 is made into a multi-layered structure (for example, a three-story structure).

更に立坑1には、廃棄体Cの搬入エレベータ等の搬入に必要な各種機器、並びに処分坑道2内には、無人搬送台車Dを備えたり、無人での搬入貯蔵管理が可能なように適宜な自動搬入装置や監視装置を必要に応じて備えるようにするものである。   Further, the vertical shaft 1 is equipped with various equipment necessary for carrying in the waste C, such as an elevator, and the disposal mine 2 is equipped with an unmanned transport cart D, or appropriate so that unmanned carry-in and storage management is possible. An automatic carry-in device and a monitoring device are provided as necessary.

また放射能レベルが比較的高い低レベル放射性廃棄物の場合は、処分坑道2自体が完全遮水構造であるから、そのまま各階層の床面上に積層載置して貯蔵することが可能であるが、高レベル放射性廃棄体(キャニスタ)Cの貯蔵の場合には、集積貯蔵は困難であるから、処分坑道2の各階のコンクリート床面25に、粘土などの適宜な緩衝材で所定の厚さに貯蔵床面27を形成すると共に多数の処分孔28を設け、前記処分孔28に高レベル放射性廃棄体Cを収納保存する。   Further, in the case of low-level radioactive waste having a relatively high radioactivity level, the disposal tunnel 2 itself has a completely water-impervious structure, so that it can be stacked and stored on the floor surface of each floor as it is. However, in the case of storage of high-level radioactive waste (canister) C, accumulation storage is difficult, so the concrete floor 25 of each floor of the disposal tunnel 2 has a predetermined thickness with an appropriate cushioning material such as clay. The storage floor 27 is formed and a large number of disposal holes 28 are provided, and the high-level radioactive waste C is stored and stored in the disposal holes 28.

1 立坑
2 処分坑道
21 セグメント(一次覆工)
211 セグメント継手
212 トランスミッションストリップ
213 ホゾ
214 シール材
22 遮水層
23 二次覆工
24 処分空間
25 コンクリート床面
26 支柱
27 貯蔵床面
28 処分孔
3 掘削装置
A 岩盤
B 裏込め材
C 廃棄体
D 無人搬送台車
1 shaft 2 disposal tunnel 21 segment (primary lining)
211 Segment joint 212 Transmission strip 213 Hozo 214 Sealing material 22 Water shielding layer 23 Secondary lining 24 Disposal space 25 Concrete floor surface 26 Column 27 Storage floor surface 28 Disposal hole 3 Excavator A Rock bed B Backfill material C Waste body D Unmanned Transport cart

本発明の請求項1に係る放射性廃棄物の地下貯蔵施設は、施設構築エリア内で、適宜な距離を離して構築されると共に、シールド工法に使用される掘削装置が配置可能な径の複数の立坑と、前記各立坑間を結ぶように各立坑から枝設され、端面全周に止水シール材を装着したコンクリートセグメントによる遮水構造の一次覆工、及び前記一次覆工の内壁面に遮水シートで形成した遮水層、及び前記遮水層の内側のコンクリートによる二次覆工によって三重の完全遮水構造とした処分空間を備える多数の処分坑道とで構成することを特徴とするものである。 The radioactive waste underground storage facility according to claim 1 of the present invention is constructed at an appropriate distance in the facility construction area and has a plurality of diameters capable of arranging the excavator used in the shield method . A primary lining of a water-blocking structure with a concrete segment that is branched from each shaft so as to connect the vertical shafts to each of the vertical shafts, and is provided with a water sealing material around the entire end surface, and the inner wall surface of the primary lining. A water-impervious layer formed of a water sheet, and a plurality of disposal tunnels equipped with a disposal space having a triple water-impervious structure by secondary lining with concrete inside the water-impervious layer. It is.

また本発明の請求項4に係る放射性廃棄物の地下貯蔵施設の構築方法は、施設構築エリア内で、適宜な距離を離して所定の掘削装置が配置可能な径の立坑を所定の深さまで複数形成し、前記各立坑間を結ぶように各立坑から枝設され多数の処分坑道を、マシン掘削とコンクリートセグメントの組立によるシールド工法で構築する際に、前記セグメントの端面全周に予め止水シール材を装着して遮水構造の一次覆工を行い、前記一次覆工の内壁面に、熱溶着によって連続する遮水シートによる遮水層を形成し、前記遮水層の内側にコンクリートによる二次覆工を行って、処分坑道からの漏水及び処分坑道内への浸水を完全に遮水した三重構造の処分空間を形成してなることを特徴とするものである。 The method of constructing an underground storage facility for radioactive waste according to Claim 4 of the present invention, a plurality facility building area until the vertical shaft a predetermined depth of apart an appropriate distance predetermined drilling device positionable diameter When a large number of disposal mine shafts are branched from each shaft so as to connect between the shafts and are constructed by shield excavation by machine excavation and assembling of concrete segments, a water-stop seal is provided around the entire end surface of the segments. The material is attached to perform a primary lining of the water-blocking structure, a water-blocking layer is formed on the inner wall surface of the primary lining by a heat-shielding sheet that is continuous by thermal welding, and a concrete-coated layer is formed inside the water-blocking layer. A secondary lining is performed to form a triple-structured disposal space that completely blocks water leakage from the disposal tunnel and inundation into the disposal tunnel .

また本発明は、施設構築エリア内で適宜な距離を離して構築した複数の立坑を形成し、前記各立坑間を結ぶように設けた処分坑道を形成してなるもので、当該施設構築エリアの範囲で地形や地盤条件に合わせて立坑位置を設定し、その間を結ぶ複数の処分坑道を構築することで、複数の処分坑道の同時施工が容易に可能であり、広い処分空間の構築を効率よく行うことができる。 Further, the present invention forms a plurality of shafts constructed at an appropriate distance in the facility construction area, and forms disposal tunnels provided so as to connect the respective shafts. By setting up the shaft position according to the topography and ground conditions in the range, and constructing multiple disposal tunnels connecting between them, it is easy to simultaneously construct multiple disposal tunnels and efficiently construct a wide disposal space It can be carried out.

更に本発明の請求項2、5に係る放射性廃棄物の地下貯蔵施設及びその構築方法は、特に前記の地下貯蔵施設及びその構築方法において、特に立坑直径を約40m程度、処分坑道直径を16m程度とし、処分坑道内を多階層構造としたもので、放射性廃棄物の搬入等の廃棄体格納作業の全自動化を、階層毎に行うことが可能であり、効率的な格納作業を実現することができる。 Further, the radioactive waste underground storage facility and the construction method thereof according to claims 2 and 5 of the present invention, in particular, in the underground storage facility and construction method thereof, in particular, the shaft diameter is about 40 m and the disposal tunnel diameter is about 16 m. The disposal tunnel has a multi-layered structure, and it is possible to perform full automation of waste storage work, such as carrying in radioactive waste, for each level, realizing efficient storage work. it can.

また本発明の請求項3に係る放射性廃棄物の地下貯蔵施設は、前記の処分坑道に多階層構造を採用した際に、特に処分坑道の各階に、適宜な緩衝材で所定の厚さに形成した貯蔵床面に、高レベル放射性廃棄体用の処分孔を形成してなるもので、高レベル放射性廃棄体の大量地層処分を実現できる。 Further, the radioactive waste underground storage facility according to claim 3 of the present invention is formed to have a predetermined thickness with an appropriate cushioning material on each floor of the disposal tunnel, particularly when a multi-level structure is adopted for the disposal tunnel. A disposal hole for high-level radioactive waste is formed on the storage floor, and a large-scale geological disposal of high-level radioactive waste can be realized.

更に本発明の請求項2、5に係る放射性廃棄物の地下貯蔵施設及びその構築方法は、特に前記の地下貯蔵施設及びその構築方法において、特に立坑直径を40m程度、処分坑道直径を16m程度とし、処分坑道内を多階層構造としたもので、放射性廃棄物の搬入等の廃棄体格納作業の全自動化を、階層毎に行うことが可能であり、効率的な格納作業を実現することができる。 Further, the radioactive waste underground storage facility and the construction method thereof according to claims 2 and 5 of the present invention, in particular, in the underground storage facility and construction method thereof, in particular, the shaft diameter is about 40 m and the disposal tunnel diameter is about 16 m. The disposal tunnel has a multi-level structure, and it is possible to perform full automation of waste storage work such as carrying in radioactive waste for each level, thus realizing efficient storage work. .

Claims (8)

施設構築エリア内で、所定の掘削装置が配置可能な径の立坑と、前記立坑から適宜方向に適宜数本を枝設すると共に、端面全周に止水シール材を装着したコンクリートセグメントによる遮水構造の一次覆工、及び前記一次覆工の内壁面に遮水シートで形成した遮水層、及び前記遮水層の内側のコンクリートによる二次覆工によって三重の完全遮水構造とした処分空間を備える処分坑道とで構成することを特徴とする放射性廃棄物の地下貯蔵施設。   Within the facility construction area, a shaft with a diameter where a predetermined excavator can be placed, and several concrete branches from the shaft in an appropriate direction, and a concrete segment with a water sealant around the entire end surface. Primary lining of the structure, a water shielding layer formed of a water shielding sheet on the inner wall surface of the primary lining, and a disposal space having a triple completely water shielding structure by secondary lining with concrete inside the water shielding layer An underground storage facility for radioactive waste, characterized by comprising a disposal tunnel comprising 施設構築エリア内で適宜な距離を離して構築した複数の立坑と、前記各立坑間を結ぶように設けた複数の処分坑道で構成される請求項1記載の放射性廃棄物の地下貯蔵施設。   The underground storage facility for radioactive waste according to claim 1, comprising a plurality of vertical shafts constructed at an appropriate distance in a facility construction area, and a plurality of disposal shafts provided so as to connect the vertical shafts. 立坑直径が約40m程度、処分坑道直径が16m程度で、処分坑道内を多階層構造とした請求項1又は2記載の放射性廃棄物の地下貯蔵施設。   The underground storage facility for radioactive waste according to claim 1 or 2, wherein the shaft diameter is about 40 m, the disposal tunnel diameter is about 16 m, and the disposal tunnel has a multi-layered structure. 多階層構造の処分坑道の各階に、適宜な緩衝材で所定の厚さに形成した貯蔵床面に、高レベル放射性廃棄体用の処分孔を形成してなる請求項3記載の放射性廃棄物の地下貯蔵施設。   The radioactive waste according to claim 3, wherein a disposal hole for high-level radioactive waste is formed on each floor of the disposal gallery having a multi-layered structure on a storage floor surface having a predetermined thickness with an appropriate cushioning material. Underground storage facility. 施設構築エリア内で、所定の掘削装置が配置可能な径の立坑を所定の深さまで形成し、前記立坑からマシン掘削とコンクリートセグメントの組立によるシールド工法で処分坑道を構築する際に、前記セグメントの端面全周に予め止水シール材を装着して遮水構造の一次覆工を行い、前記一次覆工の内壁面に、熱溶着によって連続する遮水シートによる遮水層を形成し、前記遮水層の内側にコンクリートによる二次覆工を行って、三重の完全遮水構造の処分空間を形成してなることを特徴とする放射性廃棄物の地下貯蔵施設の構築方法。   In the facility construction area, a shaft with a diameter capable of placing a predetermined excavator is formed to a predetermined depth, and when constructing a disposal tunnel from the shaft using a shield excavation method by machine excavation and assembly of a concrete segment, A water-blocking structure is primary-covered by attaching a water-proof seal material to the entire circumference of the end surface in advance, and a water-blocking layer is formed on the inner wall surface of the primary lining by a heat-shielding sheet that is continuous by thermal welding. A method for constructing an underground storage facility for radioactive waste, characterized in that a secondary lining with concrete is carried out inside the water layer to form a triple completely impermeable disposal space. 施設構築エリア内で適宜な距離を離して構築した複数の立坑を形成し、前記各立坑間を結ぶように設けた処分坑道を形成してなる請求項5記載の放射性廃棄物の地下貯蔵施設の構築方法。   The underground storage facility for radioactive waste according to claim 5, wherein a plurality of shafts constructed at an appropriate distance in the facility construction area are formed, and a disposal tunnel provided so as to connect the shafts is formed. Construction method. 立坑直径が約40m程度、処分坑道直径が16m程度で、処分坑道内を多階層構造としてなる請求項5又は6記載の放射性廃棄物の地下貯蔵施設の構築方法。   The method for constructing an underground storage facility for radioactive waste according to claim 5 or 6, wherein the shaft diameter is about 40 m, the disposal tunnel diameter is about 16 m, and the disposal tunnel has a multi-level structure. 一次覆工におけるセグメントの内壁面に、セメント結晶増殖剤を塗布して緻密化処理を施してなる請求項5乃至7記載の何れかの放射性廃棄物の地下貯蔵施設の構築方法。   The construction method of the underground storage facility of the radioactive waste in any one of Claim 5 thru | or 7 which apply | coats a cement crystal growth agent to the inner wall surface of the segment in a primary lining, and performs the densification process.
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