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論文

NMRを用いたC-A-S-Hゲルの構造解析

花町 優次*; Walker, C.*; 笹本 広; 三原 守弘

NIMS微細構造解析プラットフォーム利用報告書(Internet), 2 Pages, 2023/12

放射性廃棄物の地層処分において、坑道の支保工材料等として産業副産物であるフライアッシュとシリカフュームセメントを高含有する低アルカリ性セメント(High-volume Fly ash Silica fume Cement, HFSC)の使用が検討されている。日本原子力研究開発機構では、HFSCの主成分であるカルシウムアルミニウムシリケート水和物(C-A-S-H)ゲルを合成し、その化学的な安定性を評価するための実験及びモデル化を行っている。モデル化では、合成したサンプルに含まれるC-A-S-Hゲルや合成の際に付随して生成する副鉱物の組成を把握する必要がある。このため、2020年度には、合成したサンプルを対象に$$^{27}$$Al及び$$^{29}$$Si NMRスペクトルを取得し、Al及びSiの分配状態を同定した。その結果から、合成したサンプル中のC-A-S-Hゲルの化学組成を導出した。しかしながら、浸漬期間が28日と短く、C-A-S-Hゲル以外の副鉱物の生成が多く、所期のAl/Siモル比を有するC-A-S-Hゲルの合成には至らなかった。本課題では、より浸漬期間の長い(6ヶ月)試料を対象に、同様な手法によりC-A-S-Hゲルの化学組成を導出するため、NMRスペクトルを取得した。

論文

Evolution of the reaction and alteration of granite with Ordinary Portland cement leachates; Sequential flow experiments and reactive transport modelling

Bateman, K.*; 村山 翔太*; 花町 優次*; Wilson, J.*; 瀬田 孝将*; 天野 由記; 久保田 満*; 大内 祐司*; 舘 幸男

Minerals (Internet), 12(7), p.883_1 - 883_20, 2022/07

 被引用回数:0 パーセンタイル:0.02(Geochemistry & Geophysics)

The construction of a repository for geological disposal of radioactive waste will include the use of cement-based materials. Following closure, groundwater will saturate the repository and the extensive use of cement will result in the development of a highly alkaline porewater, pH $$>$$ 12.5; this fluid will migrate into and react with the host rock. The chemistry of the fluid will evolve over time, initially high [Na] and [K], evolving to a Ca-rich fluid, and finally returning to the groundwater composition. This evolving chemistry will affect the long-term performance of the repository, altering the physical and chemical properties, including radionuclide behaviour. Understanding these changes forms the basis for predicting the long-term evolution of the repository. This study focused on the determination of the nature and extent of the chemical reaction, as well as the formation and persistence of secondary mineral phases within a granite, comparing data from sequential flow experiments with the results of reactive transport modelling. The reaction of the granite with the cement leachates resulted in small changes in pH and the precipitation of calcium aluminum silicate hydrate (C-(A-)S-H) phases of varying compositions, of greatest abundance with the Ca-rich fluid. As the system evolved, secondary C-(A-)S-H phases re-dissolved, partly replaced by zeolites. This general sequence was successfully simulated using reactive transport modelling.

論文

Evolution of the reaction and alteration of mudstone with ordinary Portland cement leachates; Sequential flow experiments and reactive-transport modelling

Bateman, K.; 村山 翔太*; 花町 優次*; Wilson, J.*; 瀬田 孝将*; 天野 由記; 久保田 満*; 大内 祐司*; 舘 幸男

Minerals (Internet), 11(9), p.1026_1 - 1026_23, 2021/09

 被引用回数:2 パーセンタイル:23.36(Geochemistry & Geophysics)

The construction of a repository for geological disposal of radioactive waste will include the use of cement-based materials. Following closure, groundwater will saturate the repository and the extensive use of cement will result in the development of a highly alkaline porewater, pH $$>$$ 12.5. This fluid will migrate into and react with the host rock. The chemistry of the fluid will evolve over time, initially high [Na] and [K], evolving to a Ca-rich fluid and finally returning to the groundwater composition. This evolving chemistry will affect the long-term performance of the repository altering the physical and chemical properties, including radionuclide behaviour. Understanding these changes forms the basis for predicting the long-term evolution of the repository. This study focused on the determination of the nature and extent of the chemical reaction; the formation and persistence of secondary mineral phases within an argillaceous mudstone, comparing both data from sequential flow experiments with the results of reactive transport modeling. The reaction of the mudstone with the cement leachates resulted in small changes in pH but the precipitation of calcium aluminium silicate hydrate (C-A-S-H) phases of varying compositions. With the change to the groundwater secondary C-(A-)S-H phases re-dissolved being replaced by secondary carbonates. This general sequence was successfully simulated by the reactive transport model simulations.

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