Japan Geoscience Union Meeting 2015

Presentation information

Oral

Symbol M (Multidisciplinary and Interdisciplinary) » M-AG Applied Geosciences

[M-AG38] Dynamics of radionuclides emitted from Fukuchima Dai-ichi Nuclear Power Plant in the environment

Tue. May 26, 2015 4:15 PM - 6:00 PM 301B (3F)

Convener:*Kazuyuki Kita(Faculty of Science, Ibaraki University), Yuichi Onda(Center for Research on Isotopes and Environmental Dynamics, University of Tsukuba), Teruyuki Nakajima(Atmosphere and Ocean Research Institute), Yasuhito Igarashi(Atmospheric Environment and Applied Meteorology Research Department, Meteorological Research Institute), Masatoshi Yamada(Institute of Radiation Emergency Medicine, Hirosaki University), Chisato Takenaka(Graduate school of bioagricultural sciences, Nagoya University), masayoshi yamamoto(Low Level Radioactivity Laboratory, Kanazawa University), Atsushi Shinohara(Graduate school of science, Osaka University), Chair:Masatoshi Yamada(Institute of Radiation Emergency Medicine, Hirosaki University)

4:30 PM - 4:45 PM

[MAG38-23] Temporal change of Fukushima-derived Cs-137 in the sediments in the waters off Fukushima and nearby Prefectures

*Masashi KUSAKABE1, Hyoe TAKATA1, Naohiko INATOMI1, Kazuyuki HASEGAWA1, Ryosuke ISONO1 (1.Marine Ecology Research Institute)

Keywords:Fukushima nuclear power plant accident, Cs-137, bottom sediment

The 137Cs derived from the Fukushima Daiichi nuclear power plant accident in seawater has been transported to the open ocean with currents and its concentration has decreased exponentially from about 200 Bq/L to several mBq/L, a little higher than the pre-accident level, in the outside of 30 km radius of the nuclear power plant. The nuclide in the sediments, however, has not shown such a steep temporal change. Thus, its distribution pattern and temporal change should be systematically studied for a long time in order to access quantitatively the impact of the accident to the coastal environment. In addition, it is necessary to explore the mechanism for temporal change of the distribution in the sediments to predict the environmental recovery in the area. Soon after the accident, Marine Ecology Research Institute has been monitoring the water off Fukushima and nearby Prefectures for the radioactivities under the contract with Ministry of Education, Culture, Sports, Science and Technology (currently with the Nuclear Regulation Authority). We will introduce the distributions of Fukushima-derived 137Cs in the bottom sediments and their temporal change, and factors controlling the changes.

Methods
In the coastal waters off Miyagi, Fukushima, Ibaraki and Chiba Prefectures, bottom sediments were retrieved using a multiple corer. From May to June 2011, sediments were collected at 12 sites six times. After that, the sites were increased. Now the sampling is done 4 times a year at 32 sites. Surface 3 cm of cores were used to study the surface distributions of 137Cs. Vertical profiles of 137Cs in the sediments were also studied at selected sites. Additional parameters such as sediment grain size, contents of organic material and elemental composition were also measured.

Results
The concentrations of 137Cs in the surface sediments shows wide variation ranging from 0.8 to 540 Bq/kg-dry; Almost all of the data exceeded the level of pre-accident 5yr-average (0.87 +/- 0.41 Bq/kg) in the waters off Fukushima Pref. Proximity of the sampling site did not necessarily correspond to the higher values.
The temporal change of surface concentrations do not indicate steep decrease as that of seawater as a whole and the concentration at each sampling site varies so that it is not evident to see the temporal trend. However, geometric means calculated from Sept., 2011 to Nov. 2014 reveal the exponential decline trend from 47 Bq/kg to 17 Bq/kg.
Spatial variation of surface 137Cs concentration and its temporal change would be ascribed to several factors. The former may be related to grain size distribution of the sediment, chemical composition, riverine input from the land, and pathway of polluted water after the accident, and the latter desorption of Cs from the sediments, resuspension and subsequent lateral transportation, and bioturbation. The temporal change of vertical distributions of 137Cs do not show significant increase of the nuclide in the deeper layer, suggesting that bioturbation may not be the main factor for the surface decrease.
The detail of the spatiotemporal changes of 137Cs in the sediments and the relevant factors will be presented in the talk.

Acknowledgements
The data presented here have been obtained in the program contracted with MEXT (Mar. 2011-Mar. 2013) and NRA (Apr. 2013-Feb. 2015).