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通过柱实验测定土壤中贫铀的浸出情况。

Leaching of depleted uranium in soil as determined by column experiments.

作者信息

Schimmack W, Gerstmann U, Oeh U, Schultz W, Schramel P

机构信息

GSF-National Research Center for Environment and Health, Institute of Radiation Protection, Ingolstädter Landstr, 1, 85764, Neuherberg, Germany.

出版信息

Radiat Environ Biophys. 2005 Dec;44(3):183-91. doi: 10.1007/s00411-005-0013-4. Epub 2005 Oct 6.

Abstract

The basic features of the leachability of depleted uranium (DU) projectiles in soil was investigated by using 12 projectiles (145-294 g DU) and 16 columns installed in an air-conditioned laboratory. Two soils widely distributed in Europe, a sandy-loamy cambisol and a silty-loamy luvisol, were filled into the columns (3.3 kg dry soil each). The effluents of all columns were collected weekly during the observation period of 1 year. In 648 samples, 235U and 238U were determined by inductively coupled plasma mass spectrometry. The leaching rates of 238U from natural uranium were in general about 0.01 microg week-1 or smaller, while those of 238U from the DU munitions varied considerably and reached values of up to 100 microg week-1, for the different columns. In total, about 0.3 microg natural uranium corresponding to 20 ppm of its inventory in the soil was leached during the observation period. From the projectiles, an average of about 50 microg DU were leached corresponding to 18 ppm of the corroded DU mass (about 1.6% of the mean initial DU mass of the projectiles). Assuming that corrosion and leaching continue as observed, the mobilisation of 238U from DU munitions will last, on an average, for thousands of years in the soils investigated, while the munitions themselves will have been corroded after a much shorter time. It is proposed to use, for the investigated soil types, the mean leaching rates of the six columns with projectiles for transport calculations of 238U to the groundwater and, thus, for a better risk assessment of the water-dependent uptake pathways of DU.

摘要

通过使用12枚贫铀(DU)弹丸(145 - 294克DU)以及安装在有空调实验室中的16个土柱,对贫铀弹丸在土壤中的浸出性基本特征进行了研究。将欧洲广泛分布的两种土壤,一种是砂质壤土始成土,另一种是粉质壤土淋溶土,填入土柱(每个土柱3.3千克干土)。在为期1年的观测期内,每周收集所有土柱的流出液。在648个样本中,通过电感耦合等离子体质谱法测定了235U和238U。天然铀中238U的浸出率通常约为0.01微克/周或更低,而不同土柱中贫铀弹药中238U的浸出率差异很大,最高可达100微克/周。在观测期内,总共约0.3微克天然铀从土壤中浸出,相当于其在土壤中存量的20 ppm。从弹丸中,平均约50微克DU被浸出,相当于腐蚀的DU质量的18 ppm(约占弹丸平均初始DU质量的1.6%)。假设腐蚀和浸出如观测到的那样继续,在所研究的土壤中,贫铀弹药中238U的迁移平均将持续数千年,而弹药本身在短得多的时间后就会被腐蚀。建议针对所研究的土壤类型,使用装有弹丸的六个土柱的平均浸出率来计算238U向地下水的迁移,从而更好地评估与水相关的贫铀摄取途径的风险。

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