K. Rupali
Current Organizations / Institutes
The organizations/institutes from the scholar's latest article
Research Subjects
K. Rupali has a total of 12 co-authors. Here are the top co-authors by number of shared publications:
- Rakesh Kumar Singhal
Analytical Chemistry Division, Bhabha Atomic Research Centre, Mumbai 400085, India
2 shared publications A. G. Hegde
Environmental studies section, Health Physics Division , Bhabha Atomic Research Centre , Trombay, Mumbai-400 085 , India
1 shared publication- A. K. Ranade
Computational Radiation Physics Section, Health Physics Division, Bhabha Atomic Research Centre, Mumbai, India
1 shared publication Ajay Kumar
Environmental studies section, Health Physics Division, Bhabha Atomic Research Centre, Trombay, Mumbai-400 085, India
1 shared publication- Ajay Kumar
Department of Environmental Science, Graphic Era (Deemed to be University), Dehradun, India
1 shared publication H. S. Kushwaha
Environmental studies section, Health Physics Division , Bhabha Atomic Research Centre , Trombay, Mumbai-400 085 , India
1 shared publication
Latest Publications
- 3 June 2008
- Published by Springer Nature in Water, Air, & Soil Pollution
- Vol. 192 (1-4) , 293-302
Impact of Tropical Ecosystem on the Migrational Behavior of K-40, Cs-137, Th-232 U-238 in Perennial Plants
- 3 June 2008
- Published by Springer Nature in Water, Air, & Soil Pollution
- Vol. 192 (1-4) , 293-302
Impact of Tropical Ecosystem on the Migrational Behavior of K-40, Cs-137, Th-232 U-238 in Perennial Plants
- 25 May 2007
- Published by Oxford University Press (OUP) in Radiation Protection Dosimetry
- Vol. 124 (4) , 378-384
A non-parametric statistical analysis in the measurement of outdoor gamma exposure to the residents around Trombay
During this study, non-parametric statistical methods were used to validate the measured gamma dose rate with the calculated one, around Trombay. Portable dose rate digital gamma spectrometry system (target fieldSPEC) was used for in situ measurement of external gamma (γ) dose rate (measured) with the range of 1 nSv/h–10 Sv/h. The activity concentration of U-238, Th-232, K-40 and Cs-137 in the soil and their respective external dose-conversion factor (nSv/h/Bq/kg) was used to evaluate the gamma dose rate (calculated). Non-parametric statistical tool like Box- and -Whisker Plot, Spearman's (rho) rank Correlation coefficient, the Wilcoxon/Mann–Whitney test and χ2 distribution test have been applied for validation. The randomness or discrete behaviour of measured and calculated dose rate was obvious from the Box- and -Whisker Plot as mean and median of the two are not equal. The inter quartile range (Q3–Q1), which explains about the dispersion of measured and calculated dose rate were also evaluated and found to be 10 and 16 µSv/y, respectively. The linear association between the order of ranks of the two dose rates was established by using Spearman's (rho) rank correlation that showed a coefficient of R = +0.90 with the intercept +1.9, whereas Pearson's correlation was observed with a coefficient of R = +0.93 with the intercept −25.6. Wilcoxon/Mann-Whitney test shows that, medians of the calculated and the measured dose rate as significantly different under the assumption of null hypothesis and measured dose rate was made to the normal distribution by applying Z-statistics. Value of χ2 was calculated and found to be 284.95, which was very much greater than the critical value of χ20.05 = 43.77 at a degree of freedom 30, concluding that there is a highly significant difference between the measured and calculated dose rate at 5% significance level.
- 25 May 2007
- Published by Oxford University Press (OUP) in Radiation Protection Dosimetry
- Vol. 124 (4) , 378-384
A non-parametric statistical analysis in the measurement of outdoor gamma exposure to the residents around Trombay
During this study, non-parametric statistical methods were used to validate the measured gamma dose rate with the calculated one, around Trombay. Portable dose rate digital gamma spectrometry system (target fieldSPEC) was used for in situ measurement of external gamma (γ) dose rate (measured) with the range of 1 nSv/h–10 Sv/h. The activity concentration of U-238, Th-232, K-40 and Cs-137 in the soil and their respective external dose-conversion factor (nSv/h/Bq/kg) was used to evaluate the gamma dose rate (calculated). Non-parametric statistical tool like Box- and -Whisker Plot, Spearman's (rho) rank Correlation coefficient, the Wilcoxon/Mann–Whitney test and χ2 distribution test have been applied for validation. The randomness or discrete behaviour of measured and calculated dose rate was obvious from the Box- and -Whisker Plot as mean and median of the two are not equal. The inter quartile range (Q3–Q1), which explains about the dispersion of measured and calculated dose rate were also evaluated and found to be 10 and 16 µSv/y, respectively. The linear association between the order of ranks of the two dose rates was established by using Spearman's (rho) rank correlation that showed a coefficient of R = +0.90 with the intercept +1.9, whereas Pearson's correlation was observed with a coefficient of R = +0.93 with the intercept −25.6. Wilcoxon/Mann-Whitney test shows that, medians of the calculated and the measured dose rate as significantly different under the assumption of null hypothesis and measured dose rate was made to the normal distribution by applying Z-statistics. Value of χ2 was calculated and found to be 284.95, which was very much greater than the critical value of χ20.05 = 43.77 at a degree of freedom 30, concluding that there is a highly significant difference between the measured and calculated dose rate at 5% significance level.