Earth Science Frontiers ›› 2024, Vol. 31 ›› Issue (2): 447-471.DOI: 10.13745/j.esf.sf.2022.10.44
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LI Xi(), ZHU Guangyou*(
), LI Tingting, CHEN Zhiyong, AI Yifei, ZHANG Yan, TIAN Lianjie
Received:
2022-07-30
Revised:
2022-11-05
Online:
2024-03-25
Published:
2024-04-18
CLC Number:
LI Xi, ZHU Guangyou, LI Tingting, CHEN Zhiyong, AI Yifei, ZHANG Yan, TIAN Lianjie. Uranium isotope fractionation and application of uranium isotopes in environmental geosciences—a review[J]. Earth Science Frontiers, 2024, 31(2): 447-471.
同位素 | 半衰期/Ma | 放射性比/ (Bq·g-1) | 丰度比例/% |
---|---|---|---|
234U | 0.248 | 2.31×108 | 0.005 4 |
235U | 703.8 | 8.00×104 | 0.720 |
238U | 4 468 | 1.24×104 | 99.275 |
Table 1 Natural U isotope information
同位素 | 半衰期/Ma | 放射性比/ (Bq·g-1) | 丰度比例/% |
---|---|---|---|
234U | 0.248 | 2.31×108 | 0.005 4 |
235U | 703.8 | 8.00×104 | 0.720 |
238U | 4 468 | 1.24×104 | 99.275 |
步骤 | 加酸介质 | 体积 | 目的 |
---|---|---|---|
清洗柱 | 0.05 mol/L HCl | 20 mL | 清洗柱 |
平衡柱 | 3 mol/L HNO3 | 6 mL | |
上样 | 3 mol/L HNO3 | 10 mL | |
淋洗 | 3 mol/L HNO3 | 40 mL | 仅保留Th、U和Np |
盐酸介质 | 1 mol/L HCl | 6 mL | |
接Th,Np | 5 mol/L HCl+ 0.1 mol/L Oxalic | 20 mL | 洗掉Th、Np |
去草酸 | 5 mol/L HCl | 10 mL | |
接U | 0.05 mol/L HCl | 25 mL | 回收U |
Table 2 Separating U steps with U-TEVA resin. Modified after [16].
步骤 | 加酸介质 | 体积 | 目的 |
---|---|---|---|
清洗柱 | 0.05 mol/L HCl | 20 mL | 清洗柱 |
平衡柱 | 3 mol/L HNO3 | 6 mL | |
上样 | 3 mol/L HNO3 | 10 mL | |
淋洗 | 3 mol/L HNO3 | 40 mL | 仅保留Th、U和Np |
盐酸介质 | 1 mol/L HCl | 6 mL | |
接Th,Np | 5 mol/L HCl+ 0.1 mol/L Oxalic | 20 mL | 洗掉Th、Np |
去草酸 | 5 mol/L HCl | 10 mL | |
接U | 0.05 mol/L HCl | 25 mL | 回收U |
U同位素分馏 | 分馏机理 | 研究实例代表 | |
---|---|---|---|
氧化还原过程中 U同位素分馏 | 微生物还原 | 生物还原过程富集重同位素238U | Rademacher等[ |
非生物还原 | 无机非生物还原过程比较复杂,可富集重的238U,也可富集轻的235U,也可以不分馏 | Stirling等[ | |
吸附过程中U同位素分馏 | 吸附过程导致吸附剂富集轻同位素235U,同位素平衡分馏值约为-0.20‰;实验测定的同位素分馏与自然样品一致 | Weyer等[ | |
碳酸盐岩沉淀及 成岩过程中U 同位素分馏 | 碳酸盐岩共沉淀及生物作用的U同位素分馏 | 碳酸钙共沉淀过程存在U同位素分馏,δ238U取决于溶解态U的中性组分含量,中性组分含量越高,则分馏系数越大;生物效应影响碳酸钙中U的分馏,U同位素分馏大小取决于钙化区的开放程度 | Chen等[ |
碳酸盐岩成岩过程中U同位素分馏 | 碳酸盐岩成岩作用导致分馏,但沉积后的成岩作用未导致进一步分馏;准同生白云石化不会导致进一步U同位素分馏 | Romaniello等[ |
Table 3 U isotope fractionation mechanism
U同位素分馏 | 分馏机理 | 研究实例代表 | |
---|---|---|---|
氧化还原过程中 U同位素分馏 | 微生物还原 | 生物还原过程富集重同位素238U | Rademacher等[ |
非生物还原 | 无机非生物还原过程比较复杂,可富集重的238U,也可富集轻的235U,也可以不分馏 | Stirling等[ | |
吸附过程中U同位素分馏 | 吸附过程导致吸附剂富集轻同位素235U,同位素平衡分馏值约为-0.20‰;实验测定的同位素分馏与自然样品一致 | Weyer等[ | |
碳酸盐岩沉淀及 成岩过程中U 同位素分馏 | 碳酸盐岩共沉淀及生物作用的U同位素分馏 | 碳酸钙共沉淀过程存在U同位素分馏,δ238U取决于溶解态U的中性组分含量,中性组分含量越高,则分馏系数越大;生物效应影响碳酸钙中U的分馏,U同位素分馏大小取决于钙化区的开放程度 | Chen等[ |
碳酸盐岩成岩过程中U同位素分馏 | 碳酸盐岩成岩作用导致分馏,但沉积后的成岩作用未导致进一步分馏;准同生白云石化不会导致进一步U同位素分馏 | Romaniello等[ |
U同位素的地质应用 | 应用结果 | 后续研究方向 | 典型案例来源 | |
---|---|---|---|---|
示踪陆地表生环境中U的分布、迁移和扩散 | 示踪地 下水 | 地下水还原导致δ238U比值降低;氧化导致地下水δ238U比值升高;吸附与解析过程δ238U比值不变 | 后续还需要更加可靠且持久的地下水U污染处理手段 | 李高军等[ |
示踪 沉积物 | U同位素是示踪沉积物中U污染源和驱动力的有力工具 | 未来可以开展更为系统的、区域范围更大的表生沉积物的U同位素测试与研究 | 黄钊等[ | |
示踪大气 | U同位素示踪大气污染技术具有灵敏度高、准确性好、定性识别污染来源和定量计算污染程度的优势 | 定量源计算解析模型有待进一步建立和完善 | 欧阳洁等[ | |
重建地质历史时期中环境与生命协同演化过程 | 碳酸 盐岩 | 海相碳酸盐岩的U同位素已成为定性确定古海洋氧化状态的重要工具,并可作为定量示踪全球氧化还原状态转化时间、持续时间和程度的指标 | 需要考虑成岩等作用影响因素,成岩作用分馏效应矫正需进一步研究 | Lau等[ 等[ Rooney等[ |
黑色页岩 | 黑色页岩的U同位素极好地保存了原始U同位素信号 | 利用黑色页岩U同位素时需要准确扣除局部分馏信号;U同位素可以与其他氧化还原系统相关的示踪剂联合使用,从而提高准确性和可靠性 | 李聪颖等[ Wang等[ |
Table 4 Application of U isotopes in the field of earth environmental science
U同位素的地质应用 | 应用结果 | 后续研究方向 | 典型案例来源 | |
---|---|---|---|---|
示踪陆地表生环境中U的分布、迁移和扩散 | 示踪地 下水 | 地下水还原导致δ238U比值降低;氧化导致地下水δ238U比值升高;吸附与解析过程δ238U比值不变 | 后续还需要更加可靠且持久的地下水U污染处理手段 | 李高军等[ |
示踪 沉积物 | U同位素是示踪沉积物中U污染源和驱动力的有力工具 | 未来可以开展更为系统的、区域范围更大的表生沉积物的U同位素测试与研究 | 黄钊等[ | |
示踪大气 | U同位素示踪大气污染技术具有灵敏度高、准确性好、定性识别污染来源和定量计算污染程度的优势 | 定量源计算解析模型有待进一步建立和完善 | 欧阳洁等[ | |
重建地质历史时期中环境与生命协同演化过程 | 碳酸 盐岩 | 海相碳酸盐岩的U同位素已成为定性确定古海洋氧化状态的重要工具,并可作为定量示踪全球氧化还原状态转化时间、持续时间和程度的指标 | 需要考虑成岩等作用影响因素,成岩作用分馏效应矫正需进一步研究 | Lau等[ 等[ Rooney等[ |
黑色页岩 | 黑色页岩的U同位素极好地保存了原始U同位素信号 | 利用黑色页岩U同位素时需要准确扣除局部分馏信号;U同位素可以与其他氧化还原系统相关的示踪剂联合使用,从而提高准确性和可靠性 | 李聪颖等[ Wang等[ |
Fig.15 Vertical variation trend of δ238U and δ13C of carbonate rocks to trace redox events of Early Mississippi in North America. Modified after [118].
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