Effect of soil organic matter on the fate of Cs vertical distribution in forest soils.

Understanding the fate of the vertical distribution of radiocesium (Cs) in Japanese forest soils is key to assessing the radioecological consequences of the Fukushima Daiichi Nuclear Power Plant (FDNPP) accident. The Cs behavior in mineral soil is known to be primarily governed by interaction with clay minerals; however, some observations suggest the role of soil organic matter (SOM) in enhancing the mobility of Cs. Here we hypothesized that soil organic carbon (SOC) concentration profile determines the ultimate vertical pattern of Cs distribution in Japanese forest soils. In testing this hypothesis, we obtained soil samples that were collected before the FDNPP accident at four forest sites with varying SOC concentration profiles and quantified the detailed vertical profile of Cs inventory in the soils roughly half a century after global fallout in the early 1960 s. Results showed that the higher the SOC concentration in the soil profile, the deeper the Cs downward penetration. On the basis of the data for surface soils (0-10 cm), the Cs retention ratio for each of the 2-cm thick layers was evaluated as the ratio of Cs inventory in the target soil layer to the total Cs inventory in and below the soil layer. A negative correlation was found between the ratio and SOC concentration of the layer across all soils and depths. This indicates that the ultimate fate of Cs vertical distribution can be predicted as a function of SOC concentration for Japanese forest soils, and provides further evidence for SOM effects on the mobility and bioavailability of Cs in soils.