Transfer of radiocaesium from contaminated bottom sediments to marine organisms through benthic food chains in post-Fukushima and post-Chernobyl periods

Abstract. After the earthquake and tsunami on 11 March 2011 damaged the Fukushima Dai-ichi Nuclear Power Plant (FDNPP), an accidental release of a large amount of radioactive isotopes into both the air and the ocean occurred. Measurements provided by the Japanese agencies over the past 5 years show that elevated concentrations of 137Cs still remain in sediments, benthic organisms, and demersal fishes in the coastal zone around the FDNPP. These observations indicate that there are 137Cs transfer pathways from bottom sediments to the marine organisms. To describe the transfer quantitatively, the dynamic food chain biological uptake model of radionuclides (BURN) has been extended to include benthic marine organisms. The extended model takes into account both pelagic and benthic marine organisms grouped into several classes based on their trophic level and type of species: phytoplankton, zooplankton, and fishes (two types: piscivorous and non-piscivorous) for the pelagic food chain; deposit-feeding invertebrates, demersal fishes fed by benthic invertebrates, and bottom omnivorous predators for the benthic food chain; crustaceans, mollusks, and coastal predators feeding on both pelagic and benthic organisms. Bottom invertebrates ingest organic parts of bottom sediments with adsorbed radionuclides which then migrate up through the food chain. All organisms take radionuclides directly from water as well as food. The model was implemented into the compartment model POSEIDON-R and applied to the north-western Pacific for the period of 1945–2010, and then for the period of 2011–2020 to assess the radiological consequences of 137Cs released due to the FDNPP accident. The model simulations for activity concentrations of 137Cs in both pelagic and benthic organisms in the coastal area around the FDNPP agree well with measurements for the period of 2011–2015. The decrease constant in the fitted exponential function of simulated concentration for the deposit-feeding invertebrates (0.45 yr−1) is close to the observed decrease constant in sediments (0.44 yr−1). These results strongly indicate that the gradual decrease of activity in demersal fish (decrease constant is 0.46 yr−1) is caused by the transfer of activity from organic matter deposited in bottom sediment through the deposit-feeding invertebrates. The estimated model transfer coefficient from bulk sediment to demersal fish in the model for 2012–2020 (0.13) is larger than that to the deposit-feeding invertebrates (0.07). In addition, the transfer of 137Cs through food webs for the period of 1945–2020 has been modelled for the Baltic Sea contaminated due to global fallout and from the Chernobyl accident. The model simulation results obtained with generic parameters are also in good agreement with available measurements in the Baltic Sea. Unlike the open coastal system where the FDNPP is located, the dynamics of radionuclide transfer in the Baltic Sea reach a quasi-steady state due to the slow rate in water mass exchange in this semi-enclosed basin. Obtained results indicate a substantial contribution of the benthic food chain in the long-term transfer of 137Cs from contaminated bottom sediments to marine organisms and the potential application of a generic model in different regions of the world's oceans.

[1]  R. Heling,et al.  A dynamical approach for the uptake of radionuclides in marine organisms for the POSEIDON model system , 2002 .

[2]  P. Masqué,et al.  Dispersion and fate of ⁹⁰Sr in the Northwestern Pacific and adjacent seas: global fallout and the Fukushima Dai-ichi accident. , 2014, The Science of the total environment.

[3]  R. Heling,et al.  Modification of the dynamic radionuclide uptake model BURN by salinity driven transfer parameters for the marine foodweb and its integration in POSEIDON-R , 2009 .

[4]  S. Yamasaki,et al.  Investigation of Radiocesium Translation from Contaminated Sediment to Benthic Organisms , 2015 .

[5]  Simulation of the advection–diffusion–scavenging processes for 137Cs and 239,240Pu in the Japan Sea , 2006 .

[6]  D. Kitagawa,et al.  Diets of the demersal fishes on the shelf off Iwate, northern Japan , 1995 .

[7]  S. Otosaka,et al.  Sedimentation and remobilization of radiocesium in the coastal area of Ibaraki, 70 km south of the Fukushima Dai-ichi Nuclear Power Plant , 2013, Environmental Monitoring and Assessment.

[8]  R Heling,et al.  Regional long-term model of radioactivity dispersion and fate in the Northwestern Pacific and adjacent seas: application to the Fukushima Dai-ichi accident. , 2014, Journal of environmental radioactivity.

[9]  Jota Kanda,et al.  Continuing 137 Cs release to the sea from the Fukushima Dai-ichi Nuclear Power Plant through 2012 , 2013 .

[10]  J. Lawrence Edible sea urchins: biology and ecology , 2001 .

[11]  T. Flodén,et al.  Chapter 1 Geology of the Baltic Sea , 1981 .

[12]  P. Coughtrey,et al.  Radionuclide distribution and transport in terrestrial and aquatic ecosystems. A critical review of data. Volume 1. , 1983 .

[13]  Gerhard Wotawa,et al.  Xenon-133 and caesium-137 releases into the atmosphere from the Fukushima Dai-ichi nuclear power plant: determination of the source term, atmospheric dispersion, and deposition , 2011 .

[14]  K Hirose,et al.  Analysis of the 50-year records of the atmospheric deposition of long-lived radionuclides in Japan. , 2008, Applied radiation and isotopes : including data, instrumentation and methods for use in agriculture, industry and medicine.

[15]  P. Povinec,et al.  Long-term simulations of the 137Cs dispersion from the Fukushima accident in the world ocean. , 2012, Journal of environmental radioactivity.

[16]  Miho Akiyama,et al.  Biodosimetry of Restoration Workers for The Tokyo Electric Power Company (TEPCO) Fukushima Daiichi Nuclear Power Station Accident , 2013, Health physics.

[17]  M. Wood,et al.  Whole-body to tissue concentration ratios for use in biota dose assessments for animals , 2010, Radiation and environmental biophysics.

[18]  J. Vives i Batlle,et al.  Allometric methodology for the calculation of biokinetic parameters for marine biota. , 2007, The Science of the total environment.

[19]  Luigi Monte,et al.  Global analysis of the riverine transport of 90Sr and 37Cs. , 2004, Environmental science & technology.

[20]  D. Kang,et al.  Distribution of 137Cs and 239,240Pu in the surface waters of the East Sea (Sea of Japan) , 1997 .

[21]  K. Myrberg,et al.  Physical Oceanography of the Baltic Sea , 2009 .

[22]  G. Jeong,et al.  Radiocesium reaction with illite and organic matter in marine sediment. , 2006, Marine pollution bulletin.

[23]  Takaki Tsubono,et al.  Simulation of radioactive cesium transfer in the southern Fukushima coastal biota using a dynamic food chain transfer model. , 2013, Journal of environmental radioactivity.

[24]  Pavel P. Povinec,et al.  Oceanic general circulation model for the assessment of the distribution of 137Cs in the world ocean , 2003 .

[25]  R. Nakamura,et al.  Comparison of influences of sediments and sea water on accumulation of radionuclides by worms. , 1977, Journal of radiation research.

[26]  L. Cammen Ingestion rate: An empirical model for aquatic deposit feeders and detritivores , 2004, Oecologia.

[27]  S. Fowler,et al.  Rapid removal of Chernobyl fallout from Mediterranean surface waters by biological activity , 1987, Nature.

[28]  J. Kanda,et al.  Radiological impact of TEPCO's Fukushima Dai-ichi Nuclear Power Plant accident on invertebrates in the coastal benthic food web. , 2014, Journal of environmental radioactivity.

[29]  G. Schlapper Radionuclide Distribution and Transport in Terrestrial and Aquatic Ecosystems , 1986 .

[30]  Katsumi Hirose,et al.  Fukushima Accident: Radioactivity Impact on the Environment , 2013 .

[31]  T. Morita,et al.  Effects of the nuclear disaster on marine products in Fukushima. , 2013, Journal of environmental radioactivity.

[32]  Igor Brovchenko,et al.  Development and application of 3D numerical model THREETOX to the prediction of cooling water transport and mixing in the inland and coastal waters , 2008 .

[33]  P. Povinec,et al.  Pre-Fukushima Radioactivity of the Environment , 2013 .

[34]  Hideki Sawada,et al.  Five-minute resolved spatial distribution of radiocesium in sea sediment derived from the Fukushima Dai-ichi Nuclear Power Plant. , 2014, Journal of environmental radioactivity.

[35]  D LePoire,et al.  Inter-comparison of dynamic models for radionuclide transfer to marine biota in a Fukushima accident scenario. , 2016, Journal of environmental radioactivity.

[36]  F. Kasamatsu,et al.  Natural variation of radionuclide 137Cs concentration in marine organisms with special reference to the effect of food habits and trophic level , 1997 .

[37]  Irina I. Rypina,et al.  Fukushima-derived radionuclides in the ocean and biota off Japan , 2012, Proceedings of the National Academy of Sciences.

[38]  R Heling,et al.  POSEIDON/RODOS models for radiological assessment of marine environment after accidental releases: application to coastal areas of the Baltic, Black and North Seas. , 2004, Journal of environmental radioactivity.

[39]  J. Kanda,et al.  Radiocesium biokinetics in olive flounder inhabiting the Fukushima accident-affected Pacific coastal waters of eastern Japan. , 2015, Journal of environmental radioactivity.

[40]  R. Nakamura,et al.  Comparison of influences of sediments and sea water on accumulation of radionuclides by marine organisms. , 1978, Journal of radiation research.

[41]  T. Ono,et al.  Concentration of 134Cs + 137Cs bonded to the organic fraction of sediments offshore Fukushima, Japan , 2015 .

[42]  D. Hamby A review of techniques for parameter sensitivity analysis of environmental models , 1994, Environmental monitoring and assessment.

[43]  Joakim Langner,et al.  An Eulerian limited-area atmospheric transport model , 1999 .

[44]  H. Arakawa,et al.  Biological half-life of radioactive cesium in Japanese rockfish Sebastes cheni contaminated by the Fukushima Daiichi nuclear power plant accident. , 2015, Journal of environmental radioactivity.

[45]  D. Keum,et al.  A dynamic model to estimate the activity concentration and whole body dose rate of marine biota as consequences of a nuclear accident. , 2015, Journal of environmental radioactivity.

[46]  H. Sparholt Fish species interactions in the Baltic Sea [review] , 1994 .

[47]  Hyoe Takata,et al.  Spatiotemporal distributions of Fukushima-derived radionuclides in nearby marine surface sediments , 2013 .

[48]  K. Buesseler,et al.  Spatial variability and the fate of cesium in coastal sediments near Fukushima, Japan , 2014 .

[49]  S. Uchida,et al.  Ecological half-lives of radiocesium in 16 species in marine biota after the TEPCO's Fukushima Daiichi nuclear power plant accident. , 2013, Environmental science & technology.

[50]  P. Coughtrey,et al.  Radionuclide distribution and transport in terrestrial and aquatic ecosystems : a compendium of data , 1983 .

[51]  V. Maderich,et al.  A comparison of marine radionuclide dispersion models for the Baltic Sea in the frame of IAEA MODARIA program. , 2015, Journal of environmental radioactivity.

[52]  Vladimir S. Maderich,et al.  THREETOX - A Computer Code to Simulate Three-Dimensional Dispersion of Radionuclides in Stratified Water Bodies , 1997 .

[53]  P. Lam,et al.  Biomagnification of radiocesium in a marine piscivorous fish , 2001 .

[54]  M. Nakahara,et al.  Absorption of sediment-bound radionuclides through the digestive tract of marine demersal fishes. , 1978, Journal of radiation research.