Depth profiles and mobility of 129I originating from the Fukushima Dai-ichi nuclear power plant disaster under different land uses

The long-term environmental mobility of anthropogenic I-129 (physical half-life: 1.57 x 10(7) y) is of increasing concern from the view point of a low-level radiation risk assessment. A large amount of I-129 and Cs-137 (physical half-life: 30.1 y) were introduced into the environment from the Fukushima Dai-ichi Nuclear Power Plant (FDNPP) disaster. The apparent downward migration rates of the FDNPP-I-129 and-Cs-137 were estimated from their respective depth profiles on several land uses (upland field, empty lot, ground) in Fukushima. The total deposition amounts of the FDNPP-I-129 and-Cs-137 varied from 10.2 to 720 mBq/m(2) and from 18 to 1393 kBq/m(2), respectively, which swamped the regional I-129 and Cs-137 background levels in the Fukushima area. The mass depth (g/cm(2)) is employed in this study that is an indicator of the depth to which the nuclide penetrated into the soil and accounts for soil bulk density. The expectation mass depths and apparent diffusion coefficients (g(2)/cm(4)/d), derived from several depth profiles on different land uses, were 0.750-3.55 g/cm(2) and 0.090-4.8 g(2)/cm(4)/d for the FDNPP-I-129, and 0.965-4.96 g/cm(2) and 0.12-5.1 g(2)/cm(4)/d for the FDNPP-Cs-137, respectively. The expectation mass depth values of the FDNPP-I-129 were mostly greater than those of -Cs-137 at these sites. However, several anomalous cases have been found with higher expectation mass depth values of the FDNPP-Cs-137 than that of -I-129 in 4 upland fields and an empty lot. The expectation mass depth values of the FDNPP-I-129 decreased with an increase of the carbon content (%) in the topmost layer of the soil core. On the other hand, there is a weaker correlation between the FDNPP-Cs-137 and carbon content. This indicates that I-129 mainly combined with organic materials and Cs-137 is mainly combined with other soil components. The apparent diffusion coefficients D of FDNPP-I-129 and -Cs-137 were calculated using an unsteady state diffusion equation. The mobility of FDNPP-I-129 and -Cs-137 are rapidly decreased by combining with the soil components. However, some results have high D values of I-129 and Cs-137 in the soil. The difference in the soil components can produce such anomalous cases. (C) 2017 Elsevier Ltd. All rights reserved.