2021
DOI: 10.1016/j.marpolbul.2021.112491
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Spatial distribution, radiological risk assessment and positive matrix factorization of gamma-emitting radionuclides in the sediment of the Boka Kotorska Bay

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Cited by 13 publications
(7 citation statements)
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“…The mean activity concentrations of 232 Th in Jeddah marine sediments were lower than all other locations in the world except for the Arabian Gulf [48], Farasan Island [46], Oman [81], and Turkey [80]. Conversely, the 40 K mean values were higher than all other locations in the world except Addurrah beach [49], Serbia [82], Cyprus [4], and Bangladesh [32]. It is worth noting that U and Th series disequilibria were well documented [31,83].…”
Section: Activity Concentrationsmentioning
confidence: 84%
“…The mean activity concentrations of 232 Th in Jeddah marine sediments were lower than all other locations in the world except for the Arabian Gulf [48], Farasan Island [46], Oman [81], and Turkey [80]. Conversely, the 40 K mean values were higher than all other locations in the world except Addurrah beach [49], Serbia [82], Cyprus [4], and Bangladesh [32]. It is worth noting that U and Th series disequilibria were well documented [31,83].…”
Section: Activity Concentrationsmentioning
confidence: 84%
“…An ICP-MS model iCAP Q and ICP-OES model iCAP 6500, both from Thermo Scientific Inc. (Waltham, MA, USA), were employed for the instrumental measurements. The operating conditions used in this study were described previously for ICP-OES [ 53 ] and ICP-MS [ 54 ].…”
Section: Methodsmentioning
confidence: 99%
“…The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/toxics12010071/s1, Figure S1: Map of sampling locations; Table S1: Validation parameters of REY, HMs, and major elements in CFA samples using ICP-MS. The method detection limit (MDL), calibration equation, correlation coefficient (r 2 ), recovery (R), and relative standard deviation; Table S2: Ecological risk indices, the equations, and classification [53]; Table S3: Equations used in the risk assessment model [58]; Table S4: Exposure parameters and their distributions in the risk assessment model [58]; Table S5: Reference doses (RfD) (mg•kg −1 •day −1 ) and the cancer slope factors (CSF) (kg•day•mg −1 ) of HMs for ingestion, inhalation, and dermal pathway [58]; Table S6: REY concentrations (mg/kg) in CFA samples from coal-fired power plants in Serbia (mean ± SD); Table S7: Pearson correlation coefficients for the REY content in CFA samples from coal-fired power plants in Serbia; Table S8: Enrichment factor (EF) for REY in CFA; Table S9: Geoaccumulation index (Igeo) for REY in CFA; Table S10: Potential risk index (RI) for HMs in CFA; Table S11: Individual risk index (Er) for HMs and REY in CFA; Table S12: Mean hazard quotients (HQ) for REY in CFA; Table S13: Mean hazard quotients (HQ) for HMs in CFA; Table S14: Individual mean cancer risk (CR) for HMs in CFA.…”
Section: Supplementary Materialsmentioning
confidence: 99%
“…The specific activity of 226 Ra was determined from the gamma rays at 609.3, 1120.3, and 1764.5 keV of 214 Bi and 295.2 and 351.9 keV of 214 Pb. Specific activities of 40 K and 137 Cs were determined using their own 1460.8 keV and 661.7 keV gamma rays, respectively. The measured specific activity of 137 Cs was decay-corrected to the sampling date.…”
Section: Methodsmentioning
confidence: 99%