“…The radiological risks are evaluated using the activity utilization index (AUI), the gamma representative level index ( I γ ) and the excess lifetime cancer risk (ELCR), detailed in Table 4. 15,19,22,56–60…”
Section: Methods Of Experimentationmentioning
confidence: 99%
“…The radiological risks are evaluated using the activity utilization index (AUI), the gamma representative level index (I g ) and the excess lifetime cancer risk (ELCR), detailed in Table 4. 15,19,22,[56][57][58][59][60] Again, several research studies [61][62][63] have outlined the complete approach of the PMF (positive matrix factorization) model for explaining the origin of measured geo-environmental parameters as well as their quantitative contributions. Equations affiliated with the PMF model are as follows:…”
Section: Different Environmental Pollution and Radiological Indices A...mentioning
To study the geogenic processes of naturally occurring radioactive materials’ distribution, a transboundary Himalayan River (Punarbhaba) is chosen due to its trivial anthropogenic impacts. In explaining the genesis of radionuclides,...
“…The radiological risks are evaluated using the activity utilization index (AUI), the gamma representative level index ( I γ ) and the excess lifetime cancer risk (ELCR), detailed in Table 4. 15,19,22,56–60…”
Section: Methods Of Experimentationmentioning
confidence: 99%
“…The radiological risks are evaluated using the activity utilization index (AUI), the gamma representative level index (I g ) and the excess lifetime cancer risk (ELCR), detailed in Table 4. 15,19,22,[56][57][58][59][60] Again, several research studies [61][62][63] have outlined the complete approach of the PMF (positive matrix factorization) model for explaining the origin of measured geo-environmental parameters as well as their quantitative contributions. Equations affiliated with the PMF model are as follows:…”
Section: Different Environmental Pollution and Radiological Indices A...mentioning
To study the geogenic processes of naturally occurring radioactive materials’ distribution, a transboundary Himalayan River (Punarbhaba) is chosen due to its trivial anthropogenic impacts. In explaining the genesis of radionuclides,...
“…14,77,81 Aside from this, a very high correlation between typical lithophile elements Th and U (r = 0.886; p < 0.01) (Table S5 †) in this study demonstrated similar sedimentary characteristics and was hypothesized to be governed by wave hindering heavy minerals, namely monazite [(La, Ce, Nd, Th) PO 4 ] (Th-rich mineral) and zircon (ZrSiO 4 ) (U-rich mineral). 1,82 As a result, in an oxidizing environment, Th is weather-resistant (remains as insoluble Th 4+ ), but U transforms into a soluble oxyanion-complex (UO 2 ) and may easily be depleted from sediment by leaching and/or weathering. 1,14,68 Thus, U mobilization enhanced the Th/U ratio in Teesta River basin sediments, indicating monazite predominance.…”
Section: Source Identication and Provenancementioning
This study investigates ecological consequences from the combined provenance (natural and manmade) of fifteen metal(oid)s (Na, Al, K, Ti, Cr, Mn, Co, Zn, As, Rb, Sb, Cs, Ba, Th, U)...
“…Various types of physiological problems, for example, lung cancer, renal failure, kidney dysfunction, and bone deformities may be caused by exposure to NORMs" [5,6,7]. "NORMs distributions in differential environmental constituents (e.g., dust (particulate matter), sediment, soil, water) mostly depend on climatic conditions, local geology, & weathering processes" [8,9,10]. "NORMs' occurrence in soil and/or sediment is mostly correlated with external exposure to radiation if the inhalation of gaseous radon is overlooked.…”
Evaluation of Radionuclide contents of suspended particulate matter from two quarry sites in Nigeria, have been carried out using High Volume air sampler and Gamma ray spectrometer NaI (Tl) Detector. The results obtained showed the mean value for 226 Ra, 232Th and 40k for Ishiagu sampleswere 2.76, 1.57 and 5.29 Bq/Kg respectively while that obtained in Okpella sampleswere 1.84, 2.21 and 6.2 Bq/kg respectively. The values obtained were higher than their control values but lower than the world recommended safe values. The results obtained in Okpella are slightly higher than that obtained in Ishiagu sites. This could be due to different geological constituents and other mining activities going on at Okpella that might have contributed to the slight change. All the radiological health risk parameter estimated were within their safe values as recommended by UNSCEAR. Comparison of results with other similar works shows positive correlation. We therefore conclude that inhalable suspended particulate matter within quarry sites does not constitute immediate radiological health hazard though precaution should be taken to avoid long term accumulation that can lead to stochastic health risk.
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