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This study reports the 222Rn, 220Rn, and their progeny concentration in Shivamogga district by using SSNTD's based pin hole dosimeters and deposition-based progeny sensor. The average indoor 222Rn and 220Rn concentration varies from 8.14 to 146 Bq m−3 and 13.01 to 157 Bq m−3 with a mean value of 60.61 and 61.77 Bq m−3. The EEC for 222Rn and 220Rn ranges from 1.55 to 19 Bq m−3 and 0.44 to 6 Bq m−3 with a mean value of 7.29 and 2.66 Bq m−3. The annual average equilibrium factor for 222Rn is well within the global mean values of 0.4, while the thoron is bit higher than specified global mean values of 0.02. The annual effective dose varies from 0.31 to 2.5 mSvy−1 with a mean value of 1.1 mSvy−1. [ABSTRACT FROM AUTHOR]

The primary goal of this study was to determine the risk due to radon concentration in drinking water. Water is essential for most of the life on the Earth, and the quality of drinking water is a key criterion for one's health. Radon (222Rn) and radium (226Ra) are the radioactive elements that can be found in water. Thirty samples of drinking water were collected in Haliyal, Joida, and Mundgod taluks of Uttara Kannada district. Emanometry technique was used to determine the concentration of 222Rn activity. The activity concentration of 222Rn in water varies between 3.78 ± 0.38 Bq l-1. and 135.96 ± 1.72 Bq l-1 with a mean value of 26.23 ± 0.65 Bq l-1. The cumulative average annual effective doses for all of the samples under investigation are well below the safe limit of 100 µSv y-1 suggested by WHO. [ABSTRACT FROM AUTHOR]

The prime objective of this study is to estimate the natural radioactivity and their associated radiological hazards in soil samples of Uttara Kannada district having different geological conditions. The 226Ra, 232Th and 40K activities were estimated using HPGe detector based gamma ray spectrometer. The average 226Ra, 232Th and 40K activity concentrations are 36.13 ± 0.96, 48.47 ± 1.26 and 415.76 ± 6.83 Bq kg−1 respectively. The mean annual effective dose equivalent value was found to be 0.40 mSv y−1 and is less than the ICRP proposed value of 1 mSv y−1. The radiological hazard indices were computed and compared with internationally agreed values. [ABSTRACT FROM AUTHOR]

This study reports the gamma absorbed dose rate (GADR) in 88 locations within five different geological regions of Uttara Kannada district. The measurements were made using a UR-705 environmental radiation dosimeter. The outdoor gamma absorbed dose rate varies from 44.5 to 220.0 nGy h–1 with the mean value of 78.0 nGy h–1, which is 1.3 times higher than the international average value of 59 nGy h–1. The indoor gamma absorbed dose rate varies from 57.3 to 242.5 nGy h–1 with an average of 90.0 nGy h–1, which is slightly higher than the world average of 84 nGy h–1 as suggested by UNSCEAR-2000. The estimated dose rate varies with the geological background and soil type. The total AEDE ranges from 0.3 to 1.38 mSv year–1 with an average of 0.53 mSv year–1. The average total AEDE is lower than the dose limit of 1 mSv year–1 for public, suggested by ICRP-1991. [ABSTRACT FROM AUTHOR]

The 226Ra, 232Th and 40K activities were investigated in soil samples of Chikkamagaluru district, Karnataka, using γ-ray spectrometry. The average activity of 226Ra, 232Th and 40K were found to vary from 15.2 ± 0.6 to 58 ± 1.2 Bq kg−1, 14 ± 0.6 to 86.2 ± 1.7 Bq kg−1, and 224.5 ± 5.5 to 1650 ± 20.3 Bq kg−1 with a mean value of 36.93 ± 1.0, 51.6 ± 1.3 and 566.97 ± 11.0 Bq kg−1. The average activity concentrations are slightly higher than world average value. The average annual effective dose is more than the Indian average value of 0.084 mSv y−1. The average values of all the radiological hazards are less than the criterion limit. [ABSTRACT FROM AUTHOR]