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Investigation of the Environmental Fate of Tritium in the Atmosphere

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3.2 Chemical Transformations <strong>of</strong> <strong>Tritium</strong><br />

INVESTIGATION OF THE ENVIRONMENTAL FATE OF TRITIUM IN THE ATMOSPHERE<br />

Industrial tritium releases predom<strong>in</strong>antly consist <strong>of</strong> HTO and HT, and under some conditions,<br />

tritiated methane (CH3T) (ATSDR, 2002; McCubb<strong>in</strong> et al., 2001). The residence times <strong>of</strong> HT<br />

and CH3T <strong>in</strong> <strong>the</strong> atmosphere are not well known, although mean values <strong>of</strong> 5 to 10 years have<br />

been estimated (e.g., Burger, 1979). Of <strong>the</strong> possible anthropogenic forms <strong>of</strong> tritium, HTO is<br />

<strong>of</strong> most <strong>in</strong>terest, s<strong>in</strong>ce it tends to be much more biologically-active than o<strong>the</strong>r forms (UN,<br />

ILO and WHO, 1983).<br />

When tritium is released as a gas (HT) or as HTO <strong>in</strong> its vapour form (such as from airborne<br />

releases), it can be concentrated by ord<strong>in</strong>ary chemical separation <strong>of</strong> hydrogen and water<br />

vapour from air. In contrast, when present as HTO <strong>in</strong> aqueous solutions (such as <strong>in</strong> liquid<br />

effluents), it is not amenable to separation and concentration by conventional waste-treatment<br />

techniques (Blomeke, 1964; Jacobs, 1968). Instead, isotopic separations are required, which<br />

may be difficult. The more satisfactory procedures <strong>of</strong> isotopic separation are usually<br />

physical <strong>in</strong> nature because mass differences result <strong>in</strong> greater relative differences <strong>in</strong> physical<br />

properties than <strong>in</strong> chemical properties (Moeller, 1954). As a result <strong>of</strong> <strong>the</strong> similarity <strong>of</strong> <strong>the</strong><br />

properties <strong>of</strong> HTO and H2O, tritium generally follows ord<strong>in</strong>ary water <strong>in</strong> process<strong>in</strong>g streams<br />

and <strong>in</strong> <strong>the</strong> environment under such conditions (Haney, 1964; Moeller, 1954).<br />

3.2.1 <strong>Tritium</strong> Transformation from HT to HTO<br />

Upon release <strong>in</strong>to <strong>the</strong> atmosphere, key removal processes for HT <strong>in</strong>clude photochemical<br />

oxidation <strong>in</strong> air and bacterial oxidation <strong>in</strong> soil, result<strong>in</strong>g <strong>in</strong> transformation to HTO (Dunstall<br />

et al., 1985a, 1985b; Hart, 2008). The atmospheric process is slow, with a half-life <strong>of</strong> > 5<br />

years, while a much higher oxidation rate occurs at <strong>the</strong> air-soil <strong>in</strong>terface with a half-life <strong>of</strong><br />

40 m<strong>in</strong>utes to 5 hours (Mishima and Steelec, 2002; McFarlane et al., 1978, 1979). The<br />

chemical reactions are:<br />

H 2+ OH H + H O<br />

2 photochemical Equation 3.3<br />

H + O 0 + M HO 2 + M (M =o<strong>the</strong>r molecule)<br />

2H 2 +O 2 H 2O bacterial<br />

Some <strong>of</strong> <strong>the</strong> HTO that is formed at <strong>the</strong> air-soil <strong>in</strong>terface is taken up by plants through <strong>the</strong>ir<br />

roots with transpiration water, and some is emitted to <strong>the</strong> atmosphere (Neil, 1991, 1992).<br />

This HTO is available for uptake by animals and humans through <strong>in</strong>halation and <strong>in</strong>gestion,<br />

as well as by plants through <strong>the</strong>ir leaves.<br />

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