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Thesis for the Degree of Doctor of Philosophy - DTU Orbit

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129 I/ 127 I in all <strong>the</strong> samples investigated here are four – five orders <strong>of</strong> magnitude higher than <strong>the</strong><br />

reported natural isotopic ratio <strong>of</strong> 129 I/ 127 I (10 -12 , Fehn et al., 2007). The ratios <strong>of</strong> 129 I/ 127 I in<br />

Fucus from Rømø were found to be in order <strong>of</strong> 10 -7 and 10 -8 in Fucus from Bornholm. Those<br />

variations may be related to different factors as <strong>for</strong> example: i) Fucus from different locations<br />

have integrated <strong>the</strong> iodine signal over different periods <strong>of</strong> time meaning that <strong>the</strong> seaweed<br />

cannot be used as a monitor <strong>of</strong> water concentration, ii) short – term variations in <strong>the</strong> discharge<br />

<strong>of</strong> radioiodine from nuclear reprocessing plants, iii) variations in transfer factors from <strong>the</strong> two<br />

reprocessing plants in this case La Hague and Sellafield.<br />

Even if fluctuating biological functions in seaweed may be compensated <strong>for</strong> by using <strong>the</strong><br />

129 I/ 127 I ratio <strong>the</strong> question still remains to what level <strong>the</strong> seaweed is reflecting an average<br />

seawater ratio. This question is particularly interesting if <strong>the</strong> uptake <strong>of</strong> iodine depends on what<br />

species it occurs in. Previous investigation (Hou et al., 2007; Hansen et al., 2011) have shown<br />

that <strong>the</strong> two isotopes does not distribute among <strong>the</strong> two species, iodate and iodide, in a similar<br />

way. This is an effect <strong>of</strong> <strong>the</strong> very slow kinetic exchange between iodide and iodate in<br />

seawater. Iodine-129 in <strong>the</strong> <strong>for</strong>m <strong>of</strong> iodide may thus remain as iodide even when <strong>the</strong> coastal<br />

water from <strong>the</strong> English Channel mixes with more open ocean water where <strong>the</strong> main fraction<br />

<strong>of</strong> stable iodine, I-127, exist in <strong>the</strong> <strong>for</strong>m <strong>of</strong> iodate. If steady state conditions occur and <strong>the</strong><br />

iodine uptake in seaweed would be <strong>the</strong> same irrespectively <strong>of</strong> species <strong>the</strong> concentration factor<br />

defined as ratio <strong>of</strong> 129 I/ 127 I (seaweed) relative 129 I/ 127 I (seawater) should be one. Using existing<br />

129 I/ 127 I data in seawater from North Sea, Kattegat and Baltic Sea (Hou et al., 2007, Hansen et<br />

al. 2011) and combining it with <strong>the</strong> 129 I/ 127 I data at corresponding years presented here yields<br />

ratios <strong>of</strong> 0.5 <strong>for</strong> North Sea (2005), 0.7 (2006) <strong>for</strong> Sou<strong>the</strong>rn Kattegat and ~1 (2007) <strong>for</strong><br />

Bornholm. Thus, <strong>the</strong> 129 I/ 127 I ratios in collected Fucus samples, closely match with<br />

corresponding data from water. The somewhat larger difference at Rømø may be an effect <strong>of</strong><br />

this location being closer to <strong>the</strong> source and <strong>the</strong> relatively short residence time <strong>of</strong> water in <strong>the</strong><br />

8

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