首页> 外文期刊>The Science of the Total Environment >Processes affecting land-surface dynamics of ~(129)I impacted by atmospheric ~(129)I releases from a spent nuclear fuel reprocessing plant
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Processes affecting land-surface dynamics of ~(129)I impacted by atmospheric ~(129)I releases from a spent nuclear fuel reprocessing plant

机译:大气中〜(129)I释放的乏核燃料后处理厂影响〜(129)I地表动力学的过程

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摘要

Terrestrial environments impacted by atmospheric releases of ~(129)I from nuclear plants become contaminated with ~(129)I; however, the relative importance of each land-surface ~(129)I-transfer pathway in the process of the contamination is not well understood. In this study, transfers of ~(129)I in an atmosphere-vegetation-soil system are modeled and incorporated into an existing land-surface model (SOLVEG-Ⅱ). The model was also applied to the observed transfer of ~(129)I at a vegetated field impacted by atmospheric releases of ~(129)I (as gaseous I_2 and CH_3I) from the Rokkasho reprocessing plant, Japan, during 2007. Results from the model calculation and inter-comparison of the results with the measured environmental samples provide insights into the relative importance of each ~(129)I-transfer pathway in the processes of ~(129)1 contamination of leaves and soil. The model calculation revealed that contamination of leaves of wild bamboo grasses was mostly caused by foliar adsorption of inorganic ~(129)I (81%) following wet deposition of ~(129)I. In contrast, accumulation of ~(129)I in the leaf due to foliar uptake of atmospheric ~(129)I_2 (2%) was lesser. Root uptake of soil ~(129)I was low, accounted for 17% of the ~(129)I of the leaf. The low root-uptake of ~(129)I in spite of the ~(129)I contained in the soil was ascribed to the fact that the most fraction (over 90%) of the soil ~(129)I existed in "soil-fixed" (not plant-available) form. Regarding the ~(129)I-transfer to the soil, wet deposition of ~(129)I was ten-fold more effective than dry deposition of atmospheric ~(129)I_2; however, the deposition of ~(129)I during the year represented only 2% of the model-assumed ~(129)I that pre-existed in the soil; indicating the importance of long-term accumulation of ~(129)I in terrestrial environments. The model calculation also revealed that root uptake of inorganic ~(129)I can be more influential than volatilization by methylation in exportation of ~(129)I from soil.
机译:受核电厂〜(129)I大气释放影响的陆地环境被〜(129)I污染;然而,每个陆地表面〜(129)I传递途径在污染过程中的相对重要性还没有得到很好的理解。在这项研究中,模拟了大气-土壤-土壤系统中〜(129)I的转移并将其纳入现有的地表模型(SOLVEG-Ⅱ)。该模型还应用于2007年日本六所庄后处理厂大气释放的〜(129)I(气态I_2和CH_3I)对植被场中〜(129)I的观测转移。模型计算以及结果与实测环境样本的相互比较,为了解〜(129)1污染叶片和土壤过程中各个〜(129)I传递途径的相对重要性提供了见识。模型计算表明,野生竹草叶片的污染主要是由〜(129)I湿沉降后无机〜(129)I(81%)的叶面吸附引起的。相反,由于大气中〜(129)I_2(2%)的叶面吸收,导致〜(129)I在叶片中的积累较少。土壤〜(129)I的根吸收低,占叶片〜(129)I的17%。尽管土壤中含有〜(129)I,但〜(129)I的根吸收率却较低,这归因于以下事实:土壤〜(129)I的大部分(超过90%)存在于“土壤”中固定”(工厂不可用)形式。关于〜(129)I向土壤的转移,〜(129)I的湿沉降比大气〜(129)I_2的干沉降有效十倍;但是,〜(129)I的干沉降过程更有效。年仅占土壤中预先存在的〜(129)I模型假设的2%;表明〜(129)I在陆地环境中长期积累的重要性。在土壤中〜(129)I的输出中,无机〜(129)I的影响比甲基化的挥发影响更大。

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