Your browser doesn't support javascript.
loading
Mostrar: 20 | 50 | 100
Resultados 1 - 3 de 3
Filtrar
Mais filtros










Base de dados
Intervalo de ano de publicação
1.
J Water Health ; 21(12): 1847-1857, 2023 Dec.
Artigo em Inglês | MEDLINE | ID: mdl-38153716

RESUMO

This study aims to determine the background levels of tritium radioisotope in drinking and seawater samples of Sinop province before the nuclear power plant was established in Sinop. In this context, a total of 174 water samples were collected, these are as follows: nine drinking water samples from the Sinop center and districts and 165 seawater samples from the seacoast from Samsun to Kastamonu. Tritium concentrations in the collected water samples were measured by the liquid scintillation counter. The minimum detectable activity for the method used was found to be 1.48 Bq/L. The tritium concentrations of the seawater and drinking water samples were found in the range of

Assuntos
Água Potável , Centrais Nucleares , Adulto , Criança , Lactente , Humanos , Trítio , Turquia
2.
J Sci Food Agric ; 92(2): 307-12, 2012 Jan 30.
Artigo em Inglês | MEDLINE | ID: mdl-21815162

RESUMO

BACKGROUND: Rize in Turkey was contaminated by the Chernobyl accident in 1986. A comprehensive study was planned and carried out to determine the radioactivity levels and heavy metal concentrations in four food categories collected in Rize in 2008, 2009 and 2010. RESULTS: Tomato showed the highest concentration of (238) U, at 9.43 ± 0.128 Bq kg(-1) , whereas the lowest concentration of 0.20 ± 0.02 Bq kg(-1) was measured in aubergine samples. The highest concentration of (232) Th was measured at 3.22 ± 0.29 Bq kg(-1) in grape samples. (40) K was found to contribute the highest activity in all the food samples. The highest activity concentration of (137) Cs was 10.20 ± 4.19 Bq kg(-1) , for parsley. The average contribution range of each of the heavy metals to the dietary intake was 0.13-9.14, 0.27-34.63, 0.05-3.62, 0.11-14.97, 0.78-8.51 and 0.01-1.57 mg, respectively, for Mn, Fe, Cu, Zn, Ni and As. CONCLUSION: The range of radioactivity levels in food samples of the present study is of no risk to public health. Heavy metal concentrations of Mn, Fe, Cu, Zn, Ni and As obtained were far below the established values by FAO/WHO limits.


Assuntos
Monitoramento Ambiental/métodos , Contaminação de Alimentos/análise , Metais Pesados/química , Poluentes Radioativos do Solo/análise , Acidente Nuclear de Chernobyl , Grão Comestível/química , Exposição Ambiental/efeitos adversos , Frutas/química , Humanos , Fatores de Tempo , Turquia , Verduras/química
3.
J Sci Food Agric ; 91(6): 987-91, 2011 Apr.
Artigo em Inglês | MEDLINE | ID: mdl-21384365

RESUMO

BACKGROUND: In this study, the activity concentrations of (232) Th, (238) U, (40) K and (137) Cs were measured in tea, cabbage, orange, kiwi and soil samples collected from different stations using gamma spectrometry with a high-purity germanium detector. RESULTS: The average activity concentrations of (232) Th, (238) U, (40) K and (137) Cs were found to be 8.2 ± 1.8, 17.3 ± 3.3, 465.8 ± 11.8 and 20.9 ± 3.8 Bq kg(-1) in food samples, and 72.4 ± 9.8, 51.1 ± 8.3, 229.3 ± 14.7 and 312.9 ± 11.5 Bq kg(-1) in farm soils, respectively. The internal effective dose to individuals and excess lifetime cancer risk from the consumption of the food type radioactivity ranged between 11.7 and 53.6 µSv y(-1) and between 0.05 × 10(-3) and 0.24 × 10(-3) , respectively. The annual external gamma effective dose and excess lifetime cancer risk in the farms due to soil radioactivity ranged between 94.1 and 139.8 µSv y(-1) and between 0.43 × 10(-3) and 0.64 × 10(-3) , respectively. The mean transfer factors of (232) Th, (238) U, (40) K and (137) Cs, from the soil to vegetables and fruit were 0.57, 0.32, 2.12 and 0.04, respectively. CONCLUSION: Annual effective gamma doses were found to be higher than the world's average in soil samples. The excess lifetime cancer risks were only found higher than the world's average in soil samples.


Assuntos
Contaminação Radioativa de Alimentos , Frutas/química , Raios gama/efeitos adversos , Neoplasias/epidemiologia , Poluentes Radioativos do Solo/análise , Chá/química , Verduras/química , Actinidia/efeitos adversos , Actinidia/química , Actinidia/metabolismo , Transporte Biológico , Brassica/efeitos adversos , Brassica/química , Brassica/metabolismo , Radioisótopos de Césio/análise , Citrus sinensis/efeitos adversos , Citrus sinensis/química , Citrus sinensis/metabolismo , Dieta/efeitos adversos , Frutas/efeitos adversos , Frutas/metabolismo , Humanos , Folhas de Planta/efeitos adversos , Folhas de Planta/química , Folhas de Planta/metabolismo , Radioisótopos de Potássio/análise , Doses de Radiação , Risco , Solo/química , Poluentes Radioativos do Solo/efeitos adversos , Poluentes Radioativos do Solo/metabolismo , Chá/efeitos adversos , Chá/metabolismo , Tório/análise , Turquia/epidemiologia , Urânio/análise , Verduras/efeitos adversos , Verduras/metabolismo
SELEÇÃO DE REFERÊNCIAS
DETALHE DA PESQUISA
...