Short Communication
Specific activity and activity ratios of radionuclides in soil collected about 20 km from the Fukushima Daiichi Nuclear Power Plant: Radionuclide release to the south and southwest

https://doi.org/10.1016/j.scitotenv.2011.07.067Get rights and content

Abstract

Soil samples at different depths (0–2, 5–7 and 10–12 cm) were collected from J Village, about 20 km south of Fukushima Daiichi Nuclear Power Plant (FNPP) to determine their radionuclide specific activities and activity ratios. The concentrations and activity ratios of 131I, 134, 136, 137Cs and 129mTe were obtained, but only trace amounts of 95Nb, 110mAg and 140La were detected which were too low to provide accurate concentrations. Radionuclides such as 95Zr, 103, 106Ru and 140Ba that were found in Chernobyl fallout, were not found in these soil samples. This suggests that noble gasses and volatile radionuclides predominated in the releases from FNPP to the terrestrial environment. The average activity ratios of 131I/137Cs, 134Cs/137Cs, 136Cs/137Cs and 129mTe/137Cs were 55, 0.90, 0.22 and 4.0 (corrected to March 11, 2011) in the 0–2 cm soil samples of April 20 and 28, 2011.

Highlights

► Soil samples were collected at about 20 km south of Fukushima Daiichi Nuclear Power Plant. ► The concentrations of 131I, 134, 136, 137Cs and 129mTe were obtained, but 103Ru was not. ► This suggests that noble gasses and volatile radionuclides predominated in the releases. ► Activity ratio of 134Cs/137Cs from the power plant to the south was abound 0.90.

Introduction

The Fukushima Daiichi Nuclear Power Plant (FNPP) lost all electricity due to a huge tsunami after the Richter-scale magnitude 9 earthquake of March 11, 2011. The water circulation systems of Units 1, 2 and 3 were severely damaged, and radionuclides were released to the environment, especially for days in the middle of March. Concentrations of the radionuclides released was not clearly known at the time these early releases; thus deposition samples were collected at National Institute of Radiological Sciences (NIRS) in Chiba City, which is located about 220 km from FNPP and radionuclides such as 132Te (decays to 132I), 131I, 134Cs, 137Cs and 136Cs were found (Tagami et al., 2011).

The released radionuclides have already been deposited on land and sea surfaces. Recently, environmental radioactivity levels in the Kanto Plain which includes Tokyo and is located south and southwest from FNPP, have become of growing concern to the public. Since 137Cs has a long half-life of 30.04 y and it is relatively easy to detect, its specific activity data will be used for the dose estimation in the future. However, it is necessary to obtain more data on the activity ratios of short-lived radionuclides to 137Cs to estimate the total dose from radionuclides released from FNPP. In this study, to measure major radionuclides released to the south and southwest from FNPP, soil sampling was conducted in J Village, located about 20 km south of FNPP on April 20, 28 and May 4, 2011.

Section snippets

Materials and methods

Soil samples, at 0–2, 5–7 and 10–12 cm depths, were collected from a flower garden of J Village on April 20, 28 and May 4, 2011. At each sampling time, one soil core sample (about 30 cm wide area) was collected using a scoop and a ruler to check depths. The hole made using the scoop was a conic form and each sample layer were collected, and soils between 2–5 and 7–10 cm depths were removed to avoid any contamination to lower layers. The second and the third collection were carried out at 2 m

Results and discussion

Fig. 1 shows gamma-ray spectra of soil samples collected before (collected in 2003 from an agricultural field in Fukushima Prefecture) and after the accident (a 0–2 cm sample from J Village, collected on April 20, 2011). Only a small peak of 137Cs from global fallout was observed in the soil collected before the accident with 80,000 s counting time (Fig. 1(A)), but many peaks from artificial radionuclides were observed after the accident with a shorter counting time of 3600 s (Fig. 1(B)). From

Conclusion

Specific radioactivities and activity ratios were determined in soil samples collected about 20 km south of FNPP. The measured activity ratio of 134Cs/137Cs was 0.9, which was higher than that observed in Chernobyl fallout. The measured activity ratios of 134Cs/137Cs were almost the same in the south and southwest areas. However, other directions would be unlikely to have the same activity ratios because of different stages in a complex series of releases and wind directions. This work offers an

Acknowledgments

The authors thank Dr. E. R. Landa (U.S. Geological Survey) and Dr. C. Kikuchi (MCK Consulting) for their valuable comments. The authors are grateful to J Village for kindly providing us with the soil samples.

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