Arndt Michael F, West Lynn E
Environmental Health Division, Wisconsin State Laboratory of Hygiene, 2601 Agriculture Drive, Madison, WI 53718, USA.
Health Phys. 2008 May;94(5):459-70. doi: 10.1097/01.HP.0000303107.20899.4a.
The gross alpha-particle activity of water samples analyzed by EPA Method 900.0 is investigated as a function of residue mass and geometry, time between sample collection and analysis, and time between sample preparation and analysis for samples containing 224Ra, 212Pb, and 226Ra. It is shown that the gross alpha-particle activity due to 224Ra and its progeny can be up to 10 times the 224Ra activity at collection time and that due to 212Pb progeny can be up to 3 times the 212Pb activity at collection time. In samples with roughly equal activities of 224Ra and 226Ra analyzed soon after collection, it is shown that the gross alpha-particle activity is approximately constant with time because the decay of 224Ra and its progeny is offset by the ingrowth of 226Ra progeny.
通过美国环境保护局(EPA)方法900.0分析的水样的总α粒子活度,作为残留质量和几何形状、样品采集与分析之间的时间以及样品制备与分析之间的时间的函数,针对含有224Ra、212Pb和226Ra的样品进行了研究。结果表明,由224Ra及其子体导致的总α粒子活度在采集时可达224Ra活度的10倍,由212Pb子体导致的总α粒子活度在采集时可达212Pb活度的3倍。在采集后不久分析的224Ra和226Ra活度大致相等的样品中,结果表明总α粒子活度随时间大致保持恒定,因为224Ra及其子体的衰变被226Ra子体的生长所抵消。