Natural radioactivity survey on soils originated from southern part of Thailand as potential sites for nuclear power plants from radiological viewpoint and risk assessment Rawiwan Kritsananuwat Hideki Arae Masahiro Fukushi Sarata Kumar Sahoo Supitcha Chanyotha Received: 11 November 2014 Ó Akade ´miai Kiado ´, Budapest, Hungary 2015 Abstract Natural radioactivity in surface soil samples collected at potential sites from southern part of Thailand to set up nuclear power plants has been investigated. 238 U and 232 Th were determined by inductively coupled plasma mass spectrometry whereas gamma-ray spectroscopy was used for 40 K determination. The activity concentrations for 238 U, 232 Th and 40 K varied in range from 4 to 122, 6 to 170 and 5 to 1,422 Bq kg -1 , respectively. The large variation of radionuclide concentrations showed heterogeneous dis- tribution that could be attributed to geological origin. The radiation hazard parameters were estimated from activity concentration of 238 U, 232 Th and 40 K in accordance with the UNSCEAR 2000. Data obtained indicated that soils in the study areas did not pose any significant radiological health hazard to the local population. Keywords Natural radionuclides Soil c-Spectroscopy ICP-MS Radiological risk Introduction Environmental radiation arising from natural and artificial sources to human are inevitable and is a continuous process [1]. The exposure of general public to ionizing radiation is mainly due to natural radiation including cosmic and ter- restrial radiation [2]. In case of terrestrial background ra- diation, the main contributor of external exposure is emitted from primordial radionuclides e.g. 238 U, 232 Th and their decay products as well as 40 K[3]. Since 238 U and 232 Th have very long half-lives and comparable to age of the earth; consequently, they exist in sufficient quantity to contribute significant radiation dose in human [4]. Their original sources in the natural environment are the Earth’s crust and mantle [5]. During weathering processes of lithosphere, rocks and minerals are transformed into parent material of soils; consequently, the radionuclides are derived from their parent rocks and deposited in soil. The concentration of primordial radionuclides in soil vary greatly depending on the nature of their parent rocks [6] (i.e. type of rocks and minerals and their abundances) as well as physical and geochemical processes (i.e. weather- ing, transportation, sorting and deposition) [7]. Igneous rocks, such as granite, contain higher radionuclide contents than sedimentary rocks. Sedimentary processes sorting weathered materials result in variations of radionuclide concentrations in different types of sedimentary rocks [8]. Furthermore, human activity, such as mining and milling [9], coal burning [10], oil and natural gas production [11], agricultural fertilizer application [12] and power generation [13] lead to elevated concentrations of natural radionu- clides in soils. Since, soil is one of the most important source of external exposure to natural radiation in humans [14, 15], evaluation of external dose and assessment of radiological risk have been estimated by various R. Kritsananuwat H. Arae S. K. Sahoo (&) Research Centre for Radiation Protection, National Institute of Radiological Sciences, 4-9-1 Anagawa, Inage, Chiba, Japan e-mail: sahoo@nirs.go.jp R. Kritsananuwat M. Fukushi Department of Radiological Science, Tokyo Metropolitan University, 7-2-10 Higashiogu, Arakawa, Tokyo, Japan R. Kritsananuwat S. Chanyotha Department of Nuclear Engineering, Chulalongkorn University, 254 Phayathai Road, Pathumwan, Bangkok, Thailand 123 J Radioanal Nucl Chem DOI 10.1007/s10967-015-3994-8