JpGU-AGU Joint Meeting 2020

講演情報

[J] 口頭発表

セッション記号 M (領域外・複数領域) » M-AG 応用地球科学

[M-AG44] 福島原発事故により放出された放射性核種の環境動態

コンビーナ:津旨 大輔(一般財団法人 電力中央研究所)、高橋 嘉夫(東京大学大学院理学系研究科地球惑星科学専攻)、恩田 裕一(筑波大学アイソトープ環境動態研究センター)、北 和之(茨城大学理学部)

[MAG44-02] 森林植物根におけるCs-137深度分布の経年変化

*高橋 純子1佐々木 拓哉1恩田 裕一1 (1.筑波大学アイソトープ環境動態研究センター)

キーワード:福島第一原子力発電所事故、森林土壌、移行係数、放射性セシウム

In 2011, large amount of radionuclides was released into the environment by the Fukushima Daiichi Nuclear Power Plant accident. In forests where decontamination is not planned, it is expected that 137Cs will circulate and remain for the long term, so understanding the behavior of 137Cs in forest soil is important in the future. Since the accident, it has been reported that the distribution of 137Cs in Fukushima forest soil has shifted downward over time. Hihara(2019) found that the contribution by rainfall infiltration water was less than 10% of the downward migration of 137Cs in forest soil (mature cedar) in Fukushima Prefecture (August 2018 to July 2018). Therefore, this study focused on the roots of forest plants as one of the factors of downward migration, and estimated the Transfer Factor (T.F. = 137Cs concentration in root / 137Cs concentration in soil) for each depth to determine the effect.

Soil was collected from a mixed forest and a younger cedar forest (440-450 kBq m-2 estimated by aircraft monitoring) in the Yamakiya district of Kawamata-town, Fukushima Prefecture using a scraper plate. The sampling intervals were 0.5 cm for a depth of 0-5 cm, 1 cm for a depth of 5-10 cm, and 5 cm for a depth of 10-20 cm. The collected sample was dried and assed through a 2 mm sieve to measure the 137Cs concentration. In addition, the roots were separated by tweezers at the time of sieving soil, the surface particles were washed away using ultrasonic waves, and divided into three based on the diameter VF < 0.5 mm < F < 2.0 mm < M), and then the 137Cs concentration was measured with a Ge semiconductor detector.

As results, the weight average of 137Cs concentrations in root at each soil depth were 0.16-6.99 [Bq / g] in 2012, 0.44-17.81 [Bq / g] in 2015, and 1.55-30.76 [Bq / g] in 2017 for mixed forest, and these in younger ceder forest were 0.02-1.18 [Bq / g] in 2012, 0.050-3.56 [Bq / g] in 2015, and 0.21-3.49 [Bq / g] in 2017. In addition, at this stage, no clear tendency of 137Cs concentration in the different root diameter was found.

In both forests, the T.F. tended to be higher at the deeper depth in each year. The reason for the difference in the transfer coefficient for each depth is considered to be the difference in root absorption ability, the difference in the exchanged amount of 137Cs in soil, and the movement of 137Cs in the plant body (translocation) for each depth. In particular, the Transfer Factor is greater than 1 at the depth of 10-20 cm, indicating that translocation has occurred. If the roots detach and decompose at each depth, this result suggests that root absorption influences the downward migration of 137Cs in soil.