Gjelsvik Runhild, Holm Elis, Kålås John Atle, Persson Bertil, Asbrink Jessica
Norwegian Radiation Protection Authority, PO Box 55, NO-1332 Østerås, Norway.
Norwegian Radiation Protection Authority, PO Box 55, NO-1332 Østerås, Norway.
J Environ Radioact. 2014 Dec;138:402-9. doi: 10.1016/j.jenvrad.2014.02.026. Epub 2014 May 5.
Wolves, lynx and wolverines are on the top of the food-chain in northern Scandinavia and Finland. (210)Po and (137)Cs have been analysed in samples of liver, kidney and muscle from 28 wolves from Sweden. In addition blood samples were taken from 27 wolves. In 9 of the wolves, samples of muscle, liver and blood were analysed for (210)Po. Samples of liver and muscle were collected from 16 lynx and 16 wolverines from Norway. The liver samples were analysed for (210)Po and (137)Cs. Only (137)Cs analyses were carried out for the muscle samples. The wolves were collected during the winter 2010 and 2011, while the samples for lynx and wolverines were all from 2011. The activity concentrations of (210)Po in wolves were higher for liver (range 20-523 Bq kg(-1) d.w.) and kidney (range 24-942 Bq kg(-1) d.w.) than muscle (range 1-43 Bq kg(-1) d.w.) and blood (range 2-54 Bq kg(-1) d.w.). Activity ratios, (210)Po/(210)Pb, in wolf samples of muscle, liver and blood were in the ranges 2-77, 9-56 and 2-54. Using a wet weight ratio of 3.8 the maximal absorbed dose from (210)Po to wolf liver was estimated to 3500 μGy per year. Compared to wolf, the ranges of (210)Po in liver samples were lower in lynx (range 22-211 Bq kg(-1) d.w.) and wolverine (range16-160 Bq kg(-1) d.w.). Concentration of (137)Cs in wolf samples of muscle, liver, kidney and blood were in the ranges 70-8410 Bq kg(-1) d.w., 36-4050 Bq kg(-1) d.w., 31-3453 Bq kg(-1) d.w. and 4-959 Bq kg(-1) d.w., respectively. (137)Cs in lynx muscle and liver samples were in the ranges 44-13393 Bq kg(-1) d.w. and 125-10260 Bq kg(-1) d.w. The corresponding values for (137)Cs in wolverine were 22-3405 Bq kg(-1) d.w. for liver and 53-4780 Bq kg(-1) d.w. for muscle. The maximal absorbed dose from (137)Cs to lynx was estimated to 3000 μGy per year.
狼、猞猁和貂熊处于斯堪的纳维亚半岛北部和芬兰的食物链顶端。对来自瑞典的28只狼的肝脏、肾脏和肌肉样本进行了钋-210((210)Po)和铯-137((137)Cs)分析。此外,还采集了27只狼的血液样本。对其中9只狼的肌肉、肝脏和血液样本进行了钋-210分析。从挪威的16只猞猁和16只貂熊身上采集了肝脏和肌肉样本。对肝脏样本进行了钋-210和铯-137分析。仅对肌肉样本进行了铯-137分析。狼的样本采集于2010年和2011年冬季,而猞猁和貂熊的样本均来自2011年。狼体内钋-210的活度浓度在肝脏(范围为20 - 523贝克勒尔每千克干重(Bq kg(-1) d.w.))和肾脏(范围为24 - 942 Bq kg(-1) d.w.)中高于肌肉(范围为1 - 43 Bq kg(-1) d.w.)和血液(范围为2 - 54 Bq kg(-1) d.w.)。狼的肌肉、肝脏和血液样本中钋-210与铅-210((210)Pb)的活度比分别在2 - 77、9 - 56和2 - 54范围内。使用3.8的湿重比,估计钋-210对狼肝脏的最大吸收剂量为每年3500微戈瑞(μGy)。与狼相比,猞猁(范围为22 - 211 Bq kg(-1) d.w.)和貂熊(范围为16 - 160 Bq kg(-1) d.w.)肝脏样本中钋-210的范围较低。狼的肌肉、肝脏、肾脏和血液样本中铯-137的浓度分别在70 - 8410 Bq kg(-1) d.w.、36 - 4050 Bq kg(-1) d.w.、31 - 3453 Bq kg(-1) d.w.和4 - 959 Bq kg(-1) d.w.范围内。猞猁肌肉和肝脏样本中铯-137的浓度分别在44 - 13393 Bq kg(-1) d.w.和125 - 10260 Bq kg(-1) d.w.范围内。貂熊肝脏和肌肉中铯-137的相应值分别为22 - 3405 Bq kg(-1) d.w.和53 - 4780 Bq kg(-1) d.w.。估计铯-137对猞猁的最大吸收剂量为每年3000μGy。