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首页> 外文期刊>Journal of Radiation Research and Applied Sciences >Estimation of radionuclides concentration and average annual committed effective dose due to ingestion for some selected medicinal plants of South India
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Estimation of radionuclides concentration and average annual committed effective dose due to ingestion for some selected medicinal plants of South India

机译:估计印度南部某些药用植物因摄入而产生的放射性核素浓度和年平均承诺有效剂量

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Eight medicinal plants and soil samples from the Malnad area of Karnataka in South India (N 13°29′35.4″; E 75°18′02.4″) were analysed for activity concentrations of natural and artificial radionuclides using HPGe gamma spectrometry. The average annual committed effective dose (AACED) due to the ingestion of radionuclides from medicinal plants were also estimated. The activity concentrations of 226 Ra, 210 Pb, 232 Th, and 40 K were found to vary in the range of 32.27–60.12?Bqkg ?1 , 56.09–160.56?Bqkg ?1 , 49.61–98.46?Bqkg ?1 , and 241.57–712.85?Bqkg ?1 , respectively, in the soil samples and 2.66–11.27?Bqkg ?1 , BDL to 87.03?Bqkg ?1 , 2.42–8.72?Bqkg ?1 , and 93.79–6831.40?Bqkg ?1 , respectively, in the medicinal plants corresponding to the soil samples. The activity concentration of artificially produced radionuclide 137 Cs was BDL to 12.34?Bqkg ?1 in the soil and it was below detectable level (BDL) in all the plant samples. The soil to plant transfer factors (TF) varied from 0.07 to 0.27, BDL to 0.80, 0.04 to 0.13 and 0.17 to 23.80, respectively, for 226 Ra, 210 Pb, 232 Th, and 40 K. The AACED due to the ingestion of radionuclides from the medicinal plants varied from 0.0075 to 0.1067?mSvy ?1 . The AACED values reported in this study are much below the world average value of 0.30?mSvy ?1 for an individual. This indicates that there is no radiological health risk in using these plants for medicinal purposes. This study may also contribute data on local medicinal plants to formulate regulations related to radiological healthcare.
机译:使用HPGeγ谱仪分析了印度南部卡纳塔克邦Malnad地区(N 13°29'35.4“; E 75°18'02.4”)的八种药用植物和土壤样品的天然和人工放射性核素的活性浓度。还估计了由于从药用植物中摄入放射性核素而引起的年平均有效有效剂量(AACED)。发现226 Ra,210 Pb,232 Th和40 K的活度浓度在32.27–60.12?Bqkg?1、56.09–160.56?Bqkg?1、49.61–98.46?Bqkg?1和241.57之间变化。在土壤样品中分别为–712.85?Bqkg?1和在2.66–11.27?Bqkg?1中,BDL分别为87.03?Bqkg?1、2.42–8.72?Bqkg?1和93.79–6831.40?Bqkg?1对应于土壤样品的药用植物。人工产生的放射性核素137 Cs在土壤中的活动浓度为BDL至12.34?Bqkg?1,并且在所有植物样品中均低于可检测水平(BDL)。 226 Ra,210 Pb,232 Th和40 K的土壤到植物的转移因子(TF)分别从0.07到0.27,BDL到0.80、0.04到0.13和0.17到23.80。药用植物的放射性核素在0.0075至0.1067?mSvy?1之间变化。本研究报告的AACED值远低于个人的世界平均值0.30?mSvy?1。这表明将这些植物用于医学用途没有放射线健康风险。这项研究还可以提供有关当地药用植物的数据,以制定与放射保健有关的法规。

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