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Thesis for the Degree of Doctor of Philosophy - DTU Orbit

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Partition <strong>of</strong> iodine ( 129 I and 127 I) isotopes in soils and marine sediments<br />

Violeta Hansen a, *, Per Roos a , Ala Aldahan b,c , Xiaolin Hou a , Göran Possnert d<br />

a Risø National Laboratory <strong>for</strong> Sustainable Energy, NUK-202, Technical University <strong>of</strong> Denmark, Frederiksborgvej 399, P.O.B. 49, DK-4000 Roskilde, Denmark<br />

b Department <strong>of</strong> Earth Science, Uppsala University, SE-758 36 Uppsala, Sweden<br />

c Department <strong>of</strong> Geology, United Arab Emirates University, Al Ain, United Arab Emirates<br />

d Tandem Laboratory, Uppsala University, SE-751 21 Uppsala, Sweden<br />

article info<br />

Article history:<br />

Received 16 May 2011<br />

Received in revised <strong>for</strong>m<br />

12 July 2011<br />

Accepted 19 July 2011<br />

Available online xxx<br />

Keywords:<br />

Iodine-129, 127<br />

Speciation<br />

Iodine humic substances<br />

ICP-MS<br />

AMS<br />

1. Introduction<br />

abstract<br />

The bioavailability <strong>of</strong> radioactive pollutants in <strong>the</strong> environment<br />

plays a decisive role in relation to <strong>the</strong> environmental pollutant<br />

impact, and in particular to <strong>the</strong> internal and external doses to<br />

humans. The bioavailability <strong>of</strong> a pollutant is generally related to its<br />

speciation and accordingly, chemical species <strong>of</strong> radionuclides can<br />

be a determining factor affecting <strong>the</strong>ir environmental impact and<br />

hazard. Iodine-129 can also be released in reactor accidents due to<br />

its high volatility, and can in this context serve as a retrospective<br />

tracer shedding new light on <strong>the</strong> environmental behavior <strong>of</strong> <strong>the</strong><br />

radiologically much more important, but also much more shortlived<br />

131 I. Practices <strong>of</strong> speciation analyses <strong>for</strong> radionuclides are<br />

a relatively recent implement and <strong>the</strong> literature data are ra<strong>the</strong>r<br />

* Corresponding author. Technical University <strong>of</strong> Denmark, Risø National Laboratory<br />

<strong>for</strong> Sustainable Energy NUK-202, Frederiksborgvej 399, P.O.B. 49, 4000<br />

Røskilde, Denmark.<br />

E-mail address: violeta.hansen@risoe.dk (V. Hansen).<br />

0265-931X/$ e see front matter Ó 2011 Elsevier Ltd. All rights reserved.<br />

doi:10.1016/j.jenvrad.2011.07.005<br />

Journal <strong>of</strong> Environmental Radioactivity xxx (2011) 1e9<br />

Contents lists available at ScienceDirect<br />

Journal <strong>of</strong> Environmental Radioactivity<br />

journal homepage: www.elsevier.com/locate/jenvrad<br />

Natural organic matter, such as humic and fulvic acids and humin, plays a key role in determining <strong>the</strong><br />

fate and mobility <strong>of</strong> radioiodine in soil and sediments. The radioisotope 129 I is continuously produced and<br />

released from nuclear fuel reprocessing plants, and as a biophilic element, its environmental mobility is<br />

strongly linked to organic matter.<br />

Due to its long half-life (15.7 million years), 129 I builds up in <strong>the</strong> environment and can be traced since<br />

<strong>the</strong> beginning <strong>of</strong> <strong>the</strong> nuclear era in reservoirs such as soils and marine sediments. Never<strong>the</strong>less, partition<br />

<strong>of</strong> <strong>the</strong> isotope between <strong>the</strong> different types <strong>of</strong> organic matter in soil and sediment is rarely explored. Here<br />

we present a sequential extraction <strong>of</strong> 129 I and 127 I chemical <strong>for</strong>ms encountered in a Danish soil, a soil<br />

reference material (IAEA-375), an anoxic marine sediment from Sou<strong>the</strong>rn Norway and an oxic sediment<br />

from <strong>the</strong> Barents Sea. The different <strong>for</strong>ms <strong>of</strong> iodine are related to water soluble, exchangeable, carbonates,<br />

oxides as well as iodine bound to humic acid, fulvic acid and to humin and minerals. This is <strong>the</strong> first<br />

study to identify 129 I in humic and fulvic acid and humin. The results show that 30e56% <strong>of</strong> <strong>the</strong> total 127 I<br />

and 42e60% <strong>of</strong> <strong>the</strong> total 129 I are associated with organic matter in soil and sediment samples. At a soil/<br />

sediment pH below 5.0e5.5, 127 I and 129 I in <strong>the</strong> organic fraction associate primarily with <strong>the</strong> humic acid<br />

while at soil/sediment pH > 6 129 I was mostly found to be bound to fulvic acid. Anoxic conditions seem to<br />

increase <strong>the</strong> mobility and availability <strong>of</strong> iodine compared to oxic, while subaerial conditions (soils)<br />

reduces <strong>the</strong> availability <strong>of</strong> water soluble fraction compared to subaqueous (marine) conditions.<br />

Ó 2011 Elsevier Ltd. All rights reserved.<br />

scarce. The concentrations <strong>of</strong> <strong>the</strong> radioactive isotope 129 I have been<br />

and are still increasing in <strong>the</strong> environment since <strong>the</strong> beginning <strong>of</strong><br />

<strong>the</strong> atomic era in <strong>the</strong> late nineteen <strong>for</strong>ties (Hou et al., 2009a;<br />

Englund et al., 2010; Aldahan et al., 2007a; Lo’pez-Gutie’rrez<br />

et al., 2004). As iodine is a biophilic element its distribution in<br />

<strong>the</strong> environment merits investigation (Hou et al., 2003, 2009a;<br />

Aldahan et al., 2007a). The isotope has a half-life <strong>of</strong> (15.7 million<br />

years) and it is naturally <strong>for</strong>med by cosmic-ray-induced spallation<br />

<strong>of</strong> xenon in <strong>the</strong> upper atmosphere, spontaneous fission <strong>of</strong> 238 U and<br />

in minor quantities, by neutron bombardment <strong>of</strong> tellurium in <strong>the</strong><br />

geosphere. Thermal neutron induced fission <strong>of</strong> 235 U is ano<strong>the</strong>r<br />

minor natural source <strong>of</strong> 129 I in <strong>the</strong> lithosphere. Presently, <strong>the</strong> source<br />

<strong>of</strong> additional 129 I in <strong>the</strong> environment is mainly from human nuclear<br />

activity such as nuclear reprocessing facilities, nuclear weapons<br />

testing and accidents associated with nuclear power plants.<br />

Contributions <strong>of</strong> 129 I from nuclear weapon tests (57e63 kg <strong>of</strong> 129 I),<br />

<strong>the</strong> Chernobyl accident (1.3e6 kg<strong>of</strong> 129 I) and nuclear power plants<br />

are relatively insignificant (Hou et al., 2009a; Englund et al., 2010<br />

and Andersson et al., 2009). Discharges from nuclear reprocessing<br />

facilities into <strong>the</strong> marine and atmospheric environments represent<br />

Please cite this article in press as: Hansen, V., et al., Partition <strong>of</strong> iodine ( 129 I and 127 I) isotopes in soils and marine sediments, Journal <strong>of</strong> Environmental<br />

Radioactivity (2011), doi:10.1016/j.jenvrad.2011.07.005

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