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Periez, R.*; Bezhenar, R.*; Brovchenko, I.*; Duffa, C.*; Iosjpe, M.*; Jung, K. T.*; Kobayashi, Takuya; Lamego, F.*; Maderich, V.*; Min, B. I.*; et al.
Science of the Total Environment, 569-570, p.594 - 602, 2016/11
Times Cited Count:26 Percentile:63.48(Environmental Sciences)State-of-the art dispersion models were applied to simulate Cs dispersion from Chernobyl Nuclear Power Plant disaster fallout in the Baltic Sea and from Fukushima Daiichi Nuclear Plant releases in the Pacific Ocean after the 2011 tsunami. Models were of different nature, from box to full three-dimensional models, and included water/sediment interactions. Agreement between models was very good in the Baltic. In the case of Fukushima, results from models could be considered to be in acceptable agreement only after a model harmonization process consisting of using exactly the same forcing (water circulation and parameters) in all models. It was found that the dynamics of the considered system (magnitude and variability of currents) was essential in obtaining a good agreement between models. The difficulties in developing operative models for decision-making support in these dynamic environments were highlighted.
Yoshizawa, Michio
Hoshasen Kagaku, 46(6), p.184 - 187, 2003/06
no abstracts in English
Sakamoto, Ryuichi; Saito, Kimiaki; Tsutsumi, Masahiro; Nagaoka, Toshi
Hoken Butsuri, 36(4), p.297 - 307, 2001/12
There are many factors which affect external exposure in contaminated area: distributions of fallout, compositions of radioactive nuclides, soil conditions, depth profile of radioactivity in soil, rain fall, snow cover, radioactive decay, shielding effects of houses and other structures, de-contamination measures, and the 'occupancy factor' which accounts for the fraction of time that inhabitants spend in different locations. In this study, several important issues concerning these factors have been investigated using field measurements and computational simulations since 1992 in the Chernobyl area. The objectives of the study were: (1) The development of a mobile survey method to collect radiation data of the contaminated area over a wide area in a short time; (2) The verification of a method to infer external doses to the population; (3) The provision of basic data used for the evaluation of external dose due to gamma ray using a Monte Carlo simulation method. (4) Characteristics of the radiation fields in contaminated area. In this report, the results were summerized.
Togawa, Orihiko
JAERI-Data/Code 98-038, 21 Pages, 1998/12
no abstracts in English
Chino, Masamichi; Ishikawa, Hirohiko; Yamazawa, Hiromi; ; Moriuchi, Shigeru
JAERI 1334, 54 Pages, 1995/09
no abstracts in English
Togawa, Orihiko
JAERI-Data/Code 95-009, 35 Pages, 1995/07
no abstracts in English
Ishikawa, Hirohiko
Journal of Applied Meteorology, 34(7), p.1653 - 1665, 1995/07
no abstracts in English
Ishikawa, Hirohiko
Journal of Nuclear Science and Technology, 31(9), p.969 - 978, 1994/09
Times Cited Count:7 Percentile:56.56(Nuclear Science & Technology)no abstracts in English
Ishikawa, Hirohiko; Chino, Masamichi
Journal of Nuclear Science and Technology, 28(7), p.642 - 655, 1991/07
no abstracts in English
Ishikawa, Hirohiko
Journal of Nuclear Science and Technology, 28(6), p.535 - 546, 1991/06
no abstracts in English
KURRI-TR-298, p.13 - 21, 1987/00
no abstracts in English
; ; Yamazawa, Hiromi;
JAERI-M 86-142, 65 Pages, 1986/10
no abstracts in English
Hoken Butsuri, 21, p.285 - 294, 1986/00
no abstracts in English
Periez, R.*; Bezhenar, R.*; Brovchenko, I.*; Duffa, C.*; Iosjpe, M.*; Jung, K.-T.*; Kobayashi, Takuya; Lamego, F.*; Maderich, V.*; Min, B.-I.*; et al.
no journal, ,
State-of-the art dispersion models were applied to simulate Cs dispersion from Chernobyl nuclear power plant disaster fallout in the Baltic Sea and from Fukushima Daiichi Nuclear Plant releases in the Pacific Ocean after the 2011 tsunami. Models were of different nature, from box to full three-dimensional models, and included water/sediment interactions. Agreement between models and between models and experimental data (from HELCOM database) was very good in the Baltic. In the case of Fukushima, results from models could be considered to be in acceptable agreement only after a model harmonization process consisting of using exactly the same forcing (water circulation and parameters) in all models. It was found that the dynamics of the considered system (magnitude and variability of currents) was essential in obtaining a good agreement between models. The difficulties in developing operative models for decision-making support in these dynamic environments were highlighted.
Liu, J.; Dotsuta, Yuma; Kitagaki, Toru; Kozai, Naofumi; Onuki, Toshihiko
no journal, ,
In Fukushima Daiichi accident, molten core flowed down the structural materials and formed the fuel debris, which consists of uranium dioxide fuel, iron, zirconium, and concrete. Now the decommission of damaged nuclear plant and countermeasure of fuel debris are under discussion. It is essential to understand the current status of fuel debris and possible change during the defueling activities. Considering the appearance of microorganisms in TMI-2 and Chernobyl plant, the existence of microorganisms in Fukushima Daiichi Nuclear Power Plant was expected. Here, the microbial effect on fuel debris, specially the microbial degradation, was experimentally studied. It was found that oxidization and dissolution of iron and zirconium into the medium would mainly cause the degradation of fuel debris.