Transfer factors and effective half-lives of 134Cs and 137Cs in different environmental sample types obtained from Northern Finland: case Fukushima accident

Abstract The Fukushima NPP accident caused a small but detectable cesium fallout in northern Finland, of the order of 1 Bq/m 2 . This fallout transferred further to soil, water, flora and fauna. By using modern HPGe detector systems traces of 134 Cs from the Fukushima fallout were observed in various samples of biota. In northern Finland different types of environmental samples such as reindeer meat, berries, fish, lichens and wolf were collected during 2011–2013. The observed 134 Cs concentrations varied from 0.1 Bq/kg to a few Bq/kg. By using the known 134 Cs/ 137 Cs ratio observed in Fukushima fallout the increase of the Fukushima accident to the 137 Cs concentrations was found to vary from 0.06 % to 6.9 % depending on the sample type. The aggregated transfer factors (T ag ) and effective half-lives (T eff ) for 134 Cs and 137 Cs were also determined and then compared with known values found from earlier studies which are calculated based on the fallout from the Chernobyl accident. Generally, the T ag and T eff values determined in this study were found to agree with the values found in the earlier studies. The T eff values were sample-type specific and were found to vary from 0.91 to 2.1 years for 134 Cs and the estimates for 137 Cs ranged between 1.6 and 19 years. Interestingly, the ground lichens had the longest T eff whereas the beard lichen had the shortest. In fauna, highest T ag values were determined for wolf meat ranging between 1.0 and 2.2 m 2 /kg. In flora, the highest T ag values were determined for beard lichens, ranging from 1.9 m 2 /kg to 3.5 m 2 /kg.