Bryan S E, McDonald P, Hill R, Wilson R C
Westlakes Scientific Consulting Limited, The Princess Royal Building, Westlakes Science and Technology Park, Moor Row, Cumbria CA24 3LN, UK.
J Environ Radioact. 2008 Jan;99(1):7-19. doi: 10.1016/j.jenvrad.2007.06.008. Epub 2007 Sep 17.
Previous projects specifically aimed at performing radiological assessments in the vicinity of North Wales, investigating the presence and transfer of radionuclides from sea to land, were in 1986 and 1989. Since then, changes have occurred in the radioactive discharges from the British Nuclear Group Sellafield site. Annual discharges of (137)Cs, (238)Pu, (239,340)Pu and (241)Am have decreased markedly whereas, up until recent years, discharges of (99)Tc have increased. It is therefore desirable to quantify current transfer processes of radionuclides in the North Wales region and thus provide an update on 15-year-old studies. A field campaign was conducted collecting soil samples from 10 inland transects and air particulates on air filters from three High Volume Air Samplers, along the northern coast of Wales at Amlwch, Bangor Pier and Flint. Complementary field data relating to external gamma dose rates were collected at the soil sites. The field data generated for (137)Cs, (238)Pu, (239,340)Pu and (241)Am were consistent with what had been reported 15 years previously. Therefore, there has been no increase in the supply of these Sellafield-derived radionuclides to the terrestrial environment of the North Wales coast. The (99)Tc data in sediments were consistent with reported values within annual monitoring programmes, however, a relatively high activity concentration was measured in one sediment sample. This site was further investigated to determine the reason why such a high value was found. At present there is no clear evidence as to why this elevated concentration should be present, but the role of seaweed and its capacity in accumulating (99)Tc and transferring it to sediment is of interest. The analysis of the field samples for (99)Tc, (137)Cs, (238)Pu, (239,240)Pu and (241)Am has provided a data set that can be used for the modelling of the transfer of anthropogenic radionuclides from sea to land and its subsequent radiological implications and is reported in an accompanying paper.
此前专门针对在北威尔士附近进行放射性评估、调查放射性核素从海洋到陆地的存在及转移情况的项目分别在1986年和1989年开展。自那时起,英国核集团塞拉菲尔德核电站的放射性排放情况发生了变化。(137)铯、(238)钚、(239,340)钚和(241)镅的年排放量显著下降,而直到近年来,(99)锝的排放量一直在增加。因此,有必要对北威尔士地区当前放射性核素的转移过程进行量化,从而更新15年前的研究。开展了一次实地考察活动,沿着威尔士北部海岸的阿姆赫、班戈码头和弗林特,从10条内陆样带采集土壤样本,并从3个大容量空气采样器的空气过滤器上采集空气微粒。在土壤采样点收集了与外部伽马剂量率相关的补充实地数据。针对(137)铯、(238)钚、(239,340)钚和(241)镅生成的实地数据与15年前报告的情况一致。因此,塞拉菲尔德核电站产生的这些放射性核素向威尔士北海岸陆地环境的供应量并未增加。沉积物中的(99)锝数据与年度监测计划中的报告值一致,然而,在一个沉积物样本中测得相对较高的活度浓度。对该地点进行了进一步调查,以确定发现如此高数值的原因。目前尚无明确证据表明为何会出现这种浓度升高的情况,但海藻及其积累(99)锝并将其转移至沉积物中的能力值得关注。对(99)锝、(137)铯、(238)钚、(239,240)钚和(241)镅的实地样本分析提供了一组数据集,可用于模拟人为放射性核素从海洋到陆地的转移及其后续的放射性影响,相关内容在一篇随附论文中进行了报道。