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dc.contributor.advisor詹穎雯zh_TW
dc.contributor.advisorYin-Wen Chanen
dc.contributor.author吳灃恩zh_TW
dc.contributor.authorFeng-En Wuen
dc.date.accessioned2023-08-16T16:45:32Z-
dc.date.available2023-11-09-
dc.date.copyright2023-08-16-
dc.date.issued2023-
dc.date.submitted2023-08-09-
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dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/89011-
dc.description.abstract目前各國多以地下處置場為放射性廢棄物的最終處置建議,地下處置場為利用天然障蔽與人工障蔽為主要設計概念,利用多重障蔽將放射性廢棄物固定於處置場中以確保其長期穩定性及避免汙染物外釋,其中緩衝回填材料作為多重障壁的一環主要目的為防止地下水的入滲並避免放射性核種滲漏,膨潤土為具有膨脹性能與較佳阻水性能的一種黏土礦物,其能夠吸附輻射物質,可被當作緩衝回填材料使用。


本研究針對壓密之膨潤土進行水熱環境與乾熱環境之膨脹性能試驗,以了解作為緩衝回填材料之膨潤土熱水力偶合作用下其材料性能的變化。
本研究使用日本進口的 KUNIGEL-V1 與美國進口的 MX-80 純膨潤土試體,在乾密度為1.6 g/cm^3下於去離子水中進行水熱環境與乾熱環境下之材料性能試驗。KUNIGEL-V1與 MX-80同為鈉型膨潤土,而M土有較高的蒙脫石含量。
從試驗結果,MX-80具有較好的膨脹指數、束制膨脹壓力與較低的水力傳導度,在水熱環境下,最大膨脹率與最大膨脹壓力與常溫下相比都有提升,對於緩衝回填材料而言是有益的。在乾熱環境下,105℃與300℃乾燥加熱後之試體並沒有表現出與常溫下之試體明顯的差異,而溫度提高到500℃時可以觀察出其膨脹性能已大幅度降低,水力傳導係數度大幅度的提升,不適合用於緩衝回填材料。
鈉型膨潤土所受溫度小於300℃時,膨脹性能受影響不大,受500℃的高溫烘乾後,其內部結構發生不可逆反應,不可作為緩衝回填材料使用,
zh_TW
dc.description.abstractUnderground disposal facilities for the disposal of radioactive waste are recommended by many countries. The facilities primarily rely on natural and engineered barriers as the main design concept. Multiple barriers are used to control radioactive waste within the disposal site, ensuring long-term stability and preventing the release of contamination. Buffer and backfill materials are one of the components of the multiple barriers, aimed at preventing the infiltration of groundwater and the leakage of radioactive nuclides. Bentonite, a clay mineral with swelling properties and low water resistance, can adsorb radioactive substances and be used as buffer and backfill materials.
This study conducted tests on compacted bentonite under hydrothermal and dry-heating environments to study the variation of its swelling properties as buffer and backfill materials under thermo-hydraulic coupling effect. The test specimens used were KUNIGEL-V1 from Japan and MX-80 from the United States. The tests on material properties were conducted in deionized water, with a dry density of 1.6g/cm^3. Both KUNIGEL-V1 and MX-80 are sodium-type bentonites, in which MX-80 possesses a higher montmorillonite content.
According to the test results, MX-80 exhibited better swelling index, restrained swelling pressure, and lower hydraulic conductivity. Under the hydrothermal environment, both the maximum swelling ratio and maximum swelling pressure increased compared to those at room temperature conditions. This outcome sounds promising for buffer backfill materials. Under the dry-heating environment, the specimens stoved at 105℃ and 300℃ did not show significant differences comparing to room temperature specimens. However, stoving at 500℃, a significant reduction in swelling performance and a significant increase in hydraulic conductivity were observed, making it inappropriate to serve as buffer and backfill materials.
For sodium-type bentonite, when the temperature is below 300℃, it exhibits reversible behavior with minimal impact on swelling performance. However, when the temperature goes as high as 500℃, it undergoes irreversible changes in its internal structure and cannot be used as buffer and backfill materials.
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dc.description.tableofcontents誌謝 I
摘要 II
ABSTRACT III
目錄 IV
表目錄 XI
圖目錄 XIV
照片目錄 XXI
第一章、 緒論 1
1.1 研究動機 1
1.2 研究目的 1
1.3 研究流程圖 2
第二章、 文獻回顧 3
2.1 放射性廢棄物及其處置建議 3
2.1.1 放射性廢棄物之分類 3
1. 不具輻射危害之廢棄物(EW) 4
2. 短半衰期極低放射性廢棄物(VSLW) 4
3. 低放射性或極低放射性廢棄物(LLW、VLLW) 4
4. 中放射性廢棄物(ILW) 4
5. 高放射性廢棄物(ILW) 5
2.1.2 放射性廢棄物處置原則 6
2.1.3 放射性廢棄物處置建議 7
1. 近場範圍(The near field) 7
2. 遠場範圍(The far field) 7
3. 生物圈(The biosphere) 7
2.1.4 多重障蔽 9
1. 近場屏障 9
2. 遠場屏障 9
2.2 台灣放射性廢棄物現況 11
2.2.1 台灣放射性廢棄物現況 11
2.2.2 台灣乾式貯存計畫 12
2.2.3 台灣低放射性廢棄物最終處置計畫 13
2.2.4 台灣高放射性廢棄物最終處置計畫 13
2.3 放射性廢棄物最終處置場 14
2.3.1 放射性廢棄物最終處置場長期穩定性 14
2.3.2 放射性廢棄物最終處置場 14
1. 美國尤卡山核廢料處置場(Yucca Mountain Repository) 14
2. 瑞典放射性廢棄物處置場 16
2.4 膨潤土介紹 21
2.4.1 膨潤土簡介 21
2.4.2 礦物結構 21
1. 頁矽酸鹽礦物(phyllosilicates) 21
2. 黏土礦物 23
2.4.3 蒙脫石之性質 25
1. 組構單元 25
2. 土壤膠體 26
3. TOT層 26
4. 同晶置換 26
5. 永久電荷 26
6. 離子交換性能 26
7. 膨脹 26
8. 可交換陽離子容量(cation exchange capacity) 26
2.4.4 膨潤土的膨脹行為 27
1. 晶格膨脹 27
2. 滲透膨脹 29
3. 膨脹階段 31
2.4.5 不同溫度下膨潤土之變化 33
1. 凍結 33
2. 附著水與層間水脫除 33
3. 結構水脫除 34
4. 氧化反應 36
5. 結構破壞與重結晶 36
6. 蒙脫石伊利石化 36
2.5 多重障壁中緩衝回填材料之性能評估 37
2.5.1 緩衝回填材料介紹 37
2.5.2 緩衝材料性能之需求 37
1. 膨脹潛能(swelling potential) 37
2. 膨脹壓力(swelling pressure) 37
3. 低乾縮量(low shrinkage) 38
4. 廢棄物包件支撐(waste package support) 38
5. 應力緩衝效應(stress buffer effect) 38
6. 長期穩定性(long-term stability) 38
7. 低析離傾向(low segregation tendency) 38
8. 操作性、製造容量與高夯實效率(high efficient compactability) 38
9. 低水力傳導性(low hydraulic conductivity) 39
10. 核種遷移遲滯能力(radionuclide migration retardation capability) 39
11. 膠體過濾(colloid filtration) 39
12. 化學緩衝效應(chemical buffering effect) 39
13. 氣體滲透性(gas permeability) 39
2.5.3 國外對於緩衝材料性能之規定 40
2.6 緩衝回填材料之性能試驗與分析方法 45
2.6.1 基本性質試驗 45
2.6.2 單向度膨脹率之分析方法 46
2.6.3 束制膨脹壓力之分析方法 48
2.6.4 水力傳導度 50
2.7 影響緩衝回填材料性能之因素 52
2.7.1 膨潤土乾單位重 52
2.7.2 膨潤土含水量 52
2.7.3 膨潤土中蒙脫石含量及蒙脫石表面可交換陽離子類型 53
2.7.4 緩衝回填材料於海水、地下水環境之影響 56
2.7.5 緩衝回填材料於鹼性環境之影響 61
2.7.6 緩衝回填材料於酸性環境之影響 63
2.8 熱水力對於緩衝回填材料性能的影響 66
2.8.1 溫度評估 66
2.8.2 溫度模擬 67
2.8.3 不同溫度下緩衝回填材料之性能試驗 71
2.8.4 溫度對緩衝回填材料之緩衝回填材料性能影響 80
1. 溫度對滲透壓力的影響 80
2. 溫度對黏滯力的影響 80
3. 溫度對晶格膨脹的影響 81
4. 溫度對滲透膨脹的影響 82
5. 溫度對可交換陽離子的影響 84
第三章、 實驗計畫 85
3.1 性能試驗內容與架構 85
3.2 試驗材料與環境 86
3.2.1 試驗環境 86
3.2.2 日本山形縣KUNIGEL-V1 88
3.2.3 美國懷俄明州MX-80 88
3.2.4 試體編號 89
3.3 膨潤土基本性質試驗 89
3.3.1 阿太堡限度試驗 89
3.3.2 膨脹指數試驗 90
3.3.3 膨潤土活性試驗 90
3.3.4 膨潤土自然含水量試驗 90
3.3.5 膨潤土比重試驗 90
3.3.6 化學成分試驗 91
3.3.7 膨潤土中蒙脫石礦物含量試驗 91
3.4 膨潤土膨脹性能試驗 93
3.4.1 緩衝回填材之性能試驗規劃 93
3.4.2 單向度膨脹率試體製作 94
3.4.3 單向度膨脹率試驗 95
3.4.4 束制膨脹壓力試驗試體製作 97
3.4.5 制膨脹壓力試驗 98
3.4.6 水力傳導度試驗 100
3.5 膨潤土基本性質試驗結果 102
3.6 膨潤土蒙脫石含量測試結果 103
3.7 化學成分試驗結果 104
第四章、 試驗結果與討論 105
4.1 試驗結果與符號標示 105
4.2 膨潤土性能試驗結果 105
4.2.1 自然含水量測試結果 105
4.2.2 阿太保液性限度測試結果 108
4.2.3 膨潤土膨脹指數(Swelling Index)試驗結果 110
4.3 單向度膨脹率試驗結果 112
4.3.1 KUNIGEL-V1(K)單向度膨脹率試驗結果 112
1. K土常溫下理想乾單位重1.6g/cm^3單向度膨脹率(20℃) 113
2. K土水熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(40℃) 115
3. K土水熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(60℃) 117
4. K土乾熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(105℃) 119
5. K土乾熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(300℃) 121
6. K土乾熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(500℃) 123
7. K土常溫下不同乾單位重單向度膨脹率(20℃) 125
8. K土乾熱環境下理想乾單位重1.8g/cm^3單向度膨脹率(300℃) 127
9. K土理想乾單位重1.6g/cm^3單向度試驗數據 129
4.3.2 MX-80(M)單向度膨脹率試驗結果 130
1. M土常溫下理想乾單位重1.6g/cm^3單向度膨脹率(20℃) 131
2. M土水熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(40℃) 133
3. M土水熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(60℃) 135
4. M土乾熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(105℃) 137
5. M土乾熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(300℃) 139
6. M土乾熱環境下理想乾單位重1.6g/cm^3單向度膨脹率(500℃) 141
7. M土常溫下不同乾單位重單向度膨脹率(20℃) 143
8. M土乾熱下理想乾單位重1.8g/cm^3單向度膨脹率(300℃) 145
9. M土理想乾單位重1.6g/cm^3單向度試驗數據 147
4.3.3 單向度膨脹率試驗對乾單位重進行迴歸 148
1. 乾熱環境K土對乾單位重進行最大膨脹率回歸 149
2. 乾熱環境M土對乾單位重進行最大膨脹率回歸 149
4.3.4 K土對乾單位重進行最大膨脹率迴歸 150
4.3.5 M土對乾單位重進行最大膨脹率迴歸 152
4.3.6 單向度膨脹率迴歸線型比較與討論 154
4.3.7 單向度膨脹率總整理 157
4.4 束制膨脹壓力試驗結果 159
4.4.1 KUNIGEL-V1(K)束制膨脹壓力試驗結果 159
1. K土常溫下理想乾單位重1.6g/cm^3束制膨脹壓力(20℃) 160
2. K土水熱環境下理想乾單位重1.6g/cm^3束制膨脹壓力(60℃) 161
3. K土乾熱環境下理想乾單位重1.6g/cm^3束制膨脹壓力(105℃) 162
4. K土乾熱環境下理想乾單位重1.6g/cm^3束制膨脹壓力(300℃) 163
5. K土乾熱環境下理想乾單位重1.6g/cm^3束制膨脹壓力(500℃) 164
6. K土理想乾單位重1.6g/cm^3束制膨脹壓力試驗數據 165
4.4.2 MX-80(M)束制膨脹壓力試驗結果 167
1. M土常溫下理想乾單位重1.6g/cm^3束制膨脹壓力(20℃) 168
2. M土水熱環境下理想乾單位重1.6g/cm^3束制膨脹壓力(60℃) 169
3. M土乾熱環境下理想乾單位重1.6g/cm^3束制膨脹壓力(105℃) 170
4. M土乾熱環境下理想乾單位重1.6g/cm^3束制膨脹壓力(300℃) 171
5. M土乾熱環境下理想乾單位重1.6g/cm^3束制膨脹壓力(500℃) 172
6. M土理想乾單位重1.6g/cm^3束制膨脹壓力試驗數據 173
4.4.3 束制膨脹壓力試驗對乾單位重進行迴歸 175
1. K土對乾單位重進行最大膨脹壓力迴歸 175
2. M土對乾單位重進行最大膨脹壓力迴歸 177
4.4.4 束制膨脹壓力試驗綜合比較 179
4.5 水力傳導度試驗結果 182
4.5.1 KUNIGEL-V1(K) 水力傳導度試驗結果 182
4.5.2 MX-80(M) 水力傳導度試驗結果 184
4.5.3 水力傳導度試驗綜合比較 186
4.5.4 試驗綜合比較 188
第五章、 結論與建議 190
5.1 結論 190
5.2 建議 191
參考文獻 192
-
dc.language.isozh_TW-
dc.subject緩衝回填材料zh_TW
dc.subject水熱環境zh_TW
dc.subject膨潤土zh_TW
dc.subject放射性廢棄物處置場zh_TW
dc.subject乾熱環境zh_TW
dc.subjectradioactive wasteen
dc.subjectbuffer and backfill materialen
dc.subjecthydrothermal environmenten
dc.subjectdry-heating environmenten
dc.title膨潤土在熱水力耦合下之緩衝回填材料性能zh_TW
dc.titleThermo-hydro-mechanical effect on bentonite-based buffer and backfill materialsen
dc.typeThesis-
dc.date.schoolyear111-2-
dc.description.degree碩士-
dc.contributor.oralexamcommittee廖文正;楊仲家zh_TW
dc.contributor.oralexamcommitteeWen-Cheng Liao;Chung-Chia Yangen
dc.subject.keyword放射性廢棄物處置場,緩衝回填材料,膨潤土,水熱環境,乾熱環境,zh_TW
dc.subject.keywordradioactive waste,buffer and backfill material,hydrothermal environment,dry-heating environment,en
dc.relation.page200-
dc.identifier.doi10.6342/NTU202302606-
dc.rights.note同意授權(限校園內公開)-
dc.date.accepted2023-08-10-
dc.contributor.author-college工學院-
dc.contributor.author-dept土木工程學系-
dc.date.embargo-lift2028-08-01-
顯示於系所單位:土木工程學系

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