Low background gamma spectrometry was used to measure the radionuclides activity of <sup>238</sup>U, <sup>232</sup>Th, and <sup>235</sup>U series as well as <sup>40</sup>...Low background gamma spectrometry was used to measure the radionuclides activity of <sup>238</sup>U, <sup>232</sup>Th, and <sup>235</sup>U series as well as <sup>40</sup>K and <sup>137</sup>Cs in a sediment sample. The goal of the study was to measure the <sup>238</sup>U (63.3 keV peak of <sup>234</sup>Th;1001 keV peak of <sup>234m</sup>Pa) and <sup>235</sup>U (143.76 keV, 163.33 keV, and 205.31 keV peaks) activity by low background gamma spectrometry in sediment sample. <sup>235</sup>U activity in environmental samples is difficult to accurately measure by gamma spectrometry due to its low abundance in nature and low gamma line intensities at 143.76 keV, 163.33 keV, and 205.31 keV. We have shown that by using low background gamma spectrometry, it is possible to accurately measure the <sup>235</sup>U activity in sediment samples. The <sup>235</sup>U activity was measured without using the major peak of 185.7 keV (I<sub>γ</sub> = 57.2%) which requires interference correction from 186.21 keV of <sup>226</sup>Ra. <sup>226</sup>Ra activity was determined by measuring <sup>222</sup>Rn daughters (<sup>214</sup>Pb and <sup>214</sup>Bi). The precision and accuracy of the gamma activity measurement in the sediment sample were verified by using the HPGe detectors with Certified Reference Material (CRM) Irish Sea Sediment (IAEA-385). The results obtained for the 63.33 keV energy line of <sup>234</sup>Th are compared with the 1001 keV energy line of <sup>234m</sup>Pa. The values of <sup>238</sup>U and <sup>235</sup>U activities, as well as <sup>40</sup>K, <sup>137</sup>Cs, and <sup>226</sup>Ra, agreed with the certificate values of CRM. The results show that the <sup>238</sup>U is in equilibrium with its daughters (<sup>234</sup>Th, <sup>234m</sup>Pa, and <sup>210</sup>Pb). <sup>232</sup>Th is also in equilibrium with its daughters (<sup>228</sup>Ra, <sup>212</sup>Pb, <sup>212</sup>Bi and <sup>208</sup>Tl). <sup>235</sup>U/<sup>238</sup>U activity ratio of 0.046 ± 0.007 in the sediment is constant in nature but fluctuates due to geological processes. A value of 0.055 ± 0.008 was found in our sediment sample.展开更多
Mexico is one of the largest producers of nopal (Opuntiaficus indica). This "vegetable" is consumed on a daily basis by the Mexican population, being a source of food nutrients. Among its benefits, it is considere...Mexico is one of the largest producers of nopal (Opuntiaficus indica). This "vegetable" is consumed on a daily basis by the Mexican population, being a source of food nutrients. Among its benefits, it is considered the content of potassium, which is essential for human life and health. In this study, it analyzes the content of potassium of the Mexican cactus (Opuntiaficus indica) grown in 5 different regions in the Mexican Basin, where 67% of the nopal is produced for human consumption. The used methodology is gamma spectrometry with Hyperpure Germanium detector (HPGe) and Multichannel Analyzer (MCA) with Maestro~ software. The results show interesting aspects on the concentration of potassium in the nopal. This concentration will primarily depend on: (a) the geological characteristics of the location where the nopal was grows; (b) that potassium concentrations may vary substantially from a region to another, with the same species of nopal as a reference and (c) that this concentration may also vary from one growing season to another.展开更多
Gamma-ray spectroscopy based on a 100% efficiency hyper-pure germanium detector was used to evaluate the activity concentrations of <sup>226</sup>Ra, <sup>232</sup>Th, and <sup>40</sup...Gamma-ray spectroscopy based on a 100% efficiency hyper-pure germanium detector was used to evaluate the activity concentrations of <sup>226</sup>Ra, <sup>232</sup>Th, and <sup>40</sup>K natural radionuclides in sedimentary, conglomerate, igneous and sedi-ments rock samples collected from four different locations in Eastern desert in Egypt. The obtained activity concentrations are used to evaluate the radi-ological hazards indices, absorbed dose rate, annual effective dose equivalent in air, radium equivalent, external and internal hazard index, radiation level index, annual gonadal dose equivalent, excess lifetime cancer risk and expo-sure rate. The results show that 1) the absorbed dose rate depends on the rock type, 2) the annual effective dose equivalent in air in 71% of sample below 20 mSvy<sup>-1</sup> (permissible limit for workers), 3) the conglomerate rocks show low radioactivity level, 4) sedimentary rocks are rich in radium while igneous rocks are rich in thorium and the sediments rocks are rich in both radium and thorium.展开更多
In this study, sixteen soil and vegetable samples from Tafila district were collected and analyzed from eight locations. Measurements of specific activity of natural gamma emitter radionuclides, 23SU and 235U, in thes...In this study, sixteen soil and vegetable samples from Tafila district were collected and analyzed from eight locations. Measurements of specific activity of natural gamma emitter radionuclides, 23SU and 235U, in these samples using gamma spectrometry, with the help of Genie 2000 software. Measurements were used to calculate the soil-vegetable transfer factor, and then the external radiation dose and internal radiation dose due to radioactivity of the ingested food. The specific activity of238U and 235U in soil were found to vary from (in Bq/kg): 26-575 and 1.4-35.5, respectively. The specific activity of 238U and 235U in vegetables were found to vary from (in Bq/kg): 0.019 to 0.632 and 0.0013-0.0375, respectively. The calculated transfer factor of Z3SU and Z35U range from 5.9 × 10^-4to 14.6 × 10^-4 for 238U and 4.9 × 10^-4 to 16.1 × 10^-4 for 235U. External absorbed dose rates were calculated to be in the range from 12.42 to 266.00 nGy/h. The annual effective dose was found to vary from 28.94 to 619.78 μSv/y. The annual internal effective dose due to 23SU and 23SU for fresh weights ofvegetablesl were found to vary from 0.9 × 10^-3 to 35.1 × 10^-3 μSv/y for 238U and 0.61 × 10^-4 to 17.62 × 10^-4 μSv/y for 235U.展开更多
Twenty-eight environmental samples (eight well water, sixteen granitic rocks and four soils) were collected from different parts of Adham governorate (Adham, Haqal and Al-Jaizah), to assess the radiological hazard and...Twenty-eight environmental samples (eight well water, sixteen granitic rocks and four soils) were collected from different parts of Adham governorate (Adham, Haqal and Al-Jaizah), to assess the radiological hazard and cancer risk from different perspectives. Adham is situated in a valley between two granitic mountain chains, where much of water supply for drinking, house use and irrigation comes from wells collecting water rains. The activity concentrations of naturally occurring <sup>40</sup>K, <sup>226</sup>Ra and <sup>232</sup>Th and radionuclides were measured by gamma-ray spectrometry for all samples using RGK-1, RGU-1 and RGTh-1, IAEA reference standards issued by the International Atomic Energy Agency, for detector efficiency calibration. The measured values were utilized to evaluate the internal and external exposures both outdoors and indoors. Different standard room models were adopted for this respect to evaluate the indoor gamma-rays exposure from construction materials as well as internal exposure to radon gas emanating from them. Radon concentration indoors, exceeded the upper reference level in dwellings set at 300 Bq/m<sup>3</sup> by the world health organization, in many scenarios. The mean value of the total excess lifetime cancer risk (due to external exposure from gamma-rays) was 2.29 × 10<sup>-3</sup>, above the world average value of 1.45 × 10<sup>-3</sup>. Furthermore, the measured radon concentrations in all water samples exceeded the EPA (Environmental Protection Agency) 11.1 Bq·L<sup>-1</sup> standard for drinking water, ranging from 12 to 38 Bq·L<sup>-1</sup> with a mean value of 27 Bq·L<sup>-1</sup>. The total annual effective dose (due to inhalation and ingestion) from radon in water, ranged from 58 to 192 μSv/y (for adults) exceeding the international permissible limit of 100 μSv/y, in seven out of eight samples. According to obtained results, the internal exposure from radon in directly used water from wells, might be the major reason of any suspected radiological health hazard especially in Haqal. The second reason might be the internal exposure from indoor radon gas inhalation in poorly ventilated dwellings.展开更多
The Uranium-238 (<sup>238</sup>U), Thorium-232 (<sup>232</sup>Th) families and Potassium-40 (<sup>40</sup>K) are of terrestrial origin and contribute generally to an individual’s e...The Uranium-238 (<sup>238</sup>U), Thorium-232 (<sup>232</sup>Th) families and Potassium-40 (<sup>40</sup>K) are of terrestrial origin and contribute generally to an individual’s external exposure through our presence in this environment. They also contribute to the internal exposure through the ingestion of products and beverages such as water that are close to the earth. The aim of this work is to determine the committed effective dose or Total Indicative Dose (TID) due to gamma radioactivity of the borehole water from the Nord Riviera (NR) well field operated by the Côte d’Ivoire Water Distribution Company (SODECI) for the supply of drinking water to part of the population of Abidjan. In addition, the populations, with their habits, could use these borehole waters directly as drinking water. To this end, water samples from the seven (07) functional boreholes were collected and analyzed on a gamma spectrometry chain, equipped with an HPGe detector in the laboratory of the Radiation Protection Institute (RPI) of the GHANA Atomic Energy Commission (GAEC). The results of the specific activities of <sup>238</sup>U, <sup>232</sup>Th and <sup>40</sup>K obtained were transcribed into TID. As the natural radioactivity of the borehole water is high [1], the TIDs calculated from the activity results of the natural radionuclides<sup>238</sup>U, <sup>232</sup>Th, and <sup>40</sup>K vary for the seven boreholes from 0.150 to 0.166 mSv/yr with an average of 0.161 ± 0.034 mSv/yr. The TID of the control tower, where the borehole water is mixed and treated for household use, is equal to 0.136 ± 0.03 mSv/yr. The TIDs obtained are therefore all slightly greater than the WHO reference dose value of 0.1 mSv/yr. But all remain below the UNSCEAR reference dose of 0.29 mSv/yr.展开更多
Coal is the main energy source for electricity generation in the world. In Morocco, 37% of electricity generation comes from combustion coal in thermal power plants. This combustion process generates large amounts of ...Coal is the main energy source for electricity generation in the world. In Morocco, 37% of electricity generation comes from combustion coal in thermal power plants. This combustion process generates large amounts of fly and bottom ashes. In recent years, these ashes became a great topic of interest because of their different uses and especially in construction materials. In this work, we assess radiation risks due to natural radioactivity in samples of fly and bottom ashes collected from JLEC (Jorf Lasfar Energy Company) thermal power plant, and different analyses are performed through two nuclear techniques such as gamma spectrometry and alpha dosimetry based on the use of LR115 films detectors. Our analysis shows that <sup>226</sup>Ra activities and <sup>232</sup>Th in both ash samples are well above the permissible activity. The values of the external risk index (H<sub>ex</sub>) and internal one (H<sub>in</sub>) for these ashes are below unity, with the exception of 1.28 in fly ash for H<sub>in</sub>. The obtained values for the equivalent radium Ra<sub>eq</sub> and annual effective doses Ėin fly and bottom ashes are 324 Bq/kg and 210 Bq/kg, and 0.18 mSv/y and 0.11 mSv/y, respectively. The surface radon exhalation rates for the samples of fly and bottom ashes are 276 mBq⋅m<sup>-2</sup>⋅h<sup>-1</sup> and 381 mBq⋅m<sup>-2</sup>⋅h<sup>-1</sup>, respectively. Based on these results, we have shown that fly ash and bottom one from thermal power plant JLEC didn’t have, in any case, a health risk to the public so it can be effectively used in various construction activities.展开更多
Soils and other solid wastes from industrial areas of Nasirabad, Chattogram are usually dumped or used for land development. Information about the radioactivity level presented on these soil and wastes enables one to ...Soils and other solid wastes from industrial areas of Nasirabad, Chattogram are usually dumped or used for land development. Information about the radioactivity level presented on these soil and wastes enables one to assess any possible radiological hazard to humankind by the use of such materials. A total of 37 (31 soils and 6 solid waste) samples near from different types of industries along four kilometre range were collected. The presence and activity concentrations of naturally occurred radioactive materials (NORM) and anthropogenic radionuclides in the samples were estimated using HPGe detector of 40% relative efficiency. The activity concentration of <sup>226</sup>Ra, <sup>232</sup>Th and <sup>40</sup>K were found to be ranging from 8 ± 2 to 131 ± 18.33 with an average of 21 Bq<span style="white-space:nowrap;">·</span>kg<sup>-1</sup>, 10 ± 2.69 to 133 ± 15.96 with an average of 40 Bq<span style="white-space:nowrap;">·</span>kg<sup>-1</sup> and 81 ± 22.68 to 930 ± 260.40 with an average of 449 Bq<span style="white-space:nowrap;">·</span>kg<sup>-1</sup> respectively. Besides this, some hazard indices like, the radium equivalent activity (<em>Ra<sub>eq</sub></em>), external hazard index (<em>H<sub>ex</sub></em>), internal hazard index (<em>Hi<sub>n</sub></em>), and the activity concentration index (<em>I</em><sub>y</sub>) were calculated to assess the radiation hazard in this region. The averages of calculated hazard indices were within the normal limits, except the activity concentration index, which shows elevated values. The outcomes of this study could serve as important baseline radiological data for future epidemiological studies and environmental monitoring initiatives in the study area.展开更多
The assessment of radiological hazard due to external and internal indoor exposure was investigated for 26 raw granites collected from different granite quarries in Ranyah (KSA). The activity concentrations of <sup...The assessment of radiological hazard due to external and internal indoor exposure was investigated for 26 raw granites collected from different granite quarries in Ranyah (KSA). The activity concentrations of <sup>226</sup>Ra, <sup>232</sup>Th and <sup>40</sup>K were measured by high-resolution gamma spectrometry. Four granites were classified as “anomalous” due to their relatively high radioactivity. The averages and ranges of their activity concentrations were 667 (305 - 1120), 320 (161 - 491) and 586 (282 - 893) Bq·kg<sup>-1</sup>, respectively. The corresponding ones for all remaining 22 granites were 45 (18 - 77), 39 (16 - 73) and 1178 (954 - 1531) Bq·kg<sup>-</sup><sup>1</sup>, respectively. In accordance with new European Basic Safety Standards (BSS) directives requiring a uniform reference level for indoor external exposure to gamma rays of 1 mSv·y<sup>-</sup><sup>1</sup>, all 22 granites may be used as bulk or ornamental building materials without any restrictions. Three anomalous granites should be subjected to control to be used as bulk materials. One anomalous granite was categorized as hazardous having an activity concentration index higher than 6. All four anomalous granites exceeded the level of newly adopted reference level of 300 Bq·m<sup>-</sup><sup>3</sup> for radon indoor exposure in case of poor ventilation. Two of them exceeded even for adequate ventilation. ·展开更多
This study assesses radiation levels in soil, water and air in the Norochcholai,<span> </span><span>an area in Sri Lanka closest to the Kundankulam nuclear power plant, India which is situated in the...This study assesses radiation levels in soil, water and air in the Norochcholai,<span> </span><span>an area in Sri Lanka closest to the Kundankulam nuclear power plant, India which is situated in the North Western coast. This is important for monitoring radiation hazards </span><span><span><span style="font-family:;" "="">and</span></span></span><span><span><span style="font-family:;" "=""> will be useful in case of a nuclear accident. Superficial soil and water samples from 23 locations were analyzed by Gamma spectrometry using<span style="color:red;"> </span>HPGe detector. The activity concentrations of Th232, K40, Ra226 and Pb210 in the soil were 56.0</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq<span style="white-space:normal;">·</span>kg</span></span></span><span><span><span><span><sup><span style="font-family:;" "=""><span style="font-size:10px;">-</span>1</span></sup></span></span></span></span><span></span><span></span><span><span><span style="font-family:;" "="">, 96.0</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq</span></span></span>·<span><span><span style="font-family:;" "="">kg</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "="">, 24.0</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq<span style="white-space:normal;">·</span>kg</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "=""> and 27.0</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq<span style="white-space:normal;">·</span>kg</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "=""> respectively. Dose rate at 1</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">m height w</span></span></span><span><span><span style="font-family:;" "="">as</span></span></span><span><span><span style="font-family:;" "=""> recorded using a survey meter</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">(Automess 6150AD). Median dose rate was 0.098</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">μSv<span style="white-space:normal;">·</span>h</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "="">. The median gamma ray absorbed dose rate w</span></span></span><span><span><span style="font-family:;" "="">as</span></span></span><span><span><span style="font-family:;" "=""> 51.2 nGy<span style="white-space:normal;">·</span>h</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "="">,</span></span></span><span><span><span style="font-family:;" "=""> which is lower than the global average of 57 nGy<span style="white-space:normal;">·</span>h</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "="">. Radium equivalent activity</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">(Raeq) ranged from 30.3</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq/Kg -</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">458.3</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq/Kg and only one sample recorded the Raeq ></span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">370</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq/Kg as safe to be used in building materials. External hazardous indices of all the samples w</span></span></span><span><span><span style="font-family:;" "="">ere</span></span></span><span><span><span style="font-family:;" "=""> below 1 a</span></span></span><span><span><span style="font-family:;" "="">nd the mean annual effective dose was within the safe limit of 1</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">mSv/y. The health risk of exposure to terrestrial radiation from the soil in the area is minimal. These data could be used as baseline for radiation assessment.</span></span></span>展开更多
Knowledge of radioactivity present in polishing materials enables one to assess any possible radiological risks to human health. In this work, the radioactivity due to the presence of <sup>226</sup>Ra, <...Knowledge of radioactivity present in polishing materials enables one to assess any possible radiological risks to human health. In this work, the radioactivity due to the presence of <sup>226</sup>Ra, <sup>232</sup>Th, <sup>40</sup>K, and <sup>37</sup>Cs has been measured in polishing materials con-sumed in Saudi Arabia using gamma spectrometry with HPGe. The activity concentra-tions of <sup>226</sup>Ra, <sup>232</sup>Th, <sup>40</sup>K and <sup>137</sup>Cs ranged from 13.61 ± 0.005 to 0.60 ± 0.002, 18.43 ± 0.003 to 0.78 ± 0.001, 342.59 ± 0.009 to 2.47 ± 0.001 and 1.47 ± 0.001 to 0.55 ± 0.001 Bq/l, respectively. For <sup>226</sup>Ra and <sup>40</sup>K, the highest values are measured in stainless steel polisher. The highest values also measured in metal polisher (copper-chrome) and disinfectant cleaner and polisher sample for <sup>232</sup>Th and <sup>137</sup>Cs. Radium equivalent activ-ity due to the natural radioactivity of the investigated samples ranged from 51.37 to 1.24 Bq/l. This value is less than the recommended values in the established standards. The evaluated data were compared with the literature data. Our results indicate that no significant radiological hazards arise from using investigated samples hence quite safe to be used as polishing materials.展开更多
In this work, ten medicinal and nutritional leaves samples of <em>Hibiscus sabdariffa</em> Linn imported from Mali and Burkina Faso in C<span style="white-space:nowrap;"><span style=&quo...In this work, ten medicinal and nutritional leaves samples of <em>Hibiscus sabdariffa</em> Linn imported from Mali and Burkina Faso in C<span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">ô</span></span></span>te d’Ivoire and sold on the market were collected. The analysis of these plants using High Purity Germanium detector (HPGE) gamma spectrometry showed the activity concentrations of <sup>226</sup>Ra, <sup>232</sup>Th, and <sup>40</sup>K varied respectively in the range of (1.74 - 0.11) × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>3</sup> Bq/kg, (6.72 - 0.61) × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>4</sup> Bq/kg and (4.65 - 0.54) × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>3</sup> Bq/kg1 in the leaves of <em>H. sabdariffa</em>. The Average Annual Committed Effective Dose (AACED) values from leaves this plant varied from 251.492 × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>6</sup> to 68.133 × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>6</sup> mSv/y. These values found are below 0.30 mSv/y, the world average value for an individual. These results show that there is no radiological risk in consuming “bissap” leaves.展开更多
Objective To investigate the specific activities of gamma radionuclides in the soils around high energy accelerators,and to analyze the influence of rays emitted by nuclides with characteristic peaks at similar energy...Objective To investigate the specific activities of gamma radionuclides in the soils around high energy accelerators,and to analyze the influence of rays emitted by nuclides with characteristic peaks at similar energy points on nuclide measurement results,in order to provide reference for the accurate identification of radionuclides.Methods GR5021 high-purity germanium gamma spectroscopy system was used to measure the specific activities of gamma-emitting radionuclides 226Ra,232Th,238U,40K and artificial radionuclides 54Mn,52Mn,7Be,22Na,59Fe,95Zr in six soil samples around three kinds of high energy accelerators,and the theoretical counts of the characteristic peak of 835.7keV were compared with the measured counts of the characteristic peak of 54Mn.Results The specific activity ranges of gamma-emitting radionuclides 226Ra,232Th,238U and 40K in the soils around three kinds of high energy accelerators were 55.5–171,34.9–99.9,21.9–79.3 and 247–680 Bq/kg,respectively.The specific activities of artificial radionuclides 52Mn,7Be,22Na,59Fe and 95Zr were basically lower than the minimum detection limit.A characteristic peak was found at the energy point of 835.7keV in six soil samples,and the corresponding total absorption peak counts were from 228Ac of 232Thdecay daughter.Conclusions The specific activities of gamma-emitting radionuclides were at the normal natural background levels.The specific activities of artificial radionuclides were basically lower than the minimum detection limits.For 232Th,when its specific activity is above 40 Bq/kg,characteristic peak of its decay daughter 228Ac could be misjudged as characteristic peak of 54Mn.展开更多
Introduction Because of the increasing use of phosphate in industries worldwide,especially in Togo,it is interesting to investigate the potential radioactivity exposure of phosphate ores,especially in the one being ex...Introduction Because of the increasing use of phosphate in industries worldwide,especially in Togo,it is interesting to investigate the potential radioactivity exposure of phosphate ores,especially in the one being exploring in Togo nowadays.Material and methods The contents of natural radionuclides(40K,226Ra,232Th,235U and 238U)were assessed in phosphate soil samples from Kpogamé,Dagbati and Kpéméin the maritime region of Togo by using gamma spectrometry-based Broad Energy Germanium detector(BEGe6530).Since no study was made prior to the exploitation,the samples from the control area of Anfoin-Kpota far away from the three others were considered as reference.Results and discussion The results are discussed and compared with the data from other countries.The activity concentration of 40K,226Ra,232Th,235U and 238U are between(59.45 and 129.99),(20.19 and 779.93),(16.81 and 121.42),(2.26 and 52.03)and(16.66 and 841.14)Bq kg^(−1),respectively.The values obtained shows that the exploitation sites(Dagbati and Kpogamé)and treatment site(Kpémé)have a very high level of radioactivity than the control area(Anfoin-Kpota).The Kpogaméand Dagbati exploitation and Kpéméwaste discharging phosphate deposit sites were found to have higher activity concentration than many others exploited phosphate sedimentary deposits around the world.The average annual effective dose of the above studied sites is 0.36,0.24 and 0.48 mSv year−1,respectively.The value related to the discharge waste site is about 2%of the 1.0 mSv year−1 recommended by the International Commission on Radiological Protection as the maximum annual dose to the public.Conclusions The obtained result of both radioactivity and radiological level in the studied areas will be considered as a pre-operational baseline to estimate the possible radiological impacts due to mining and processing phosphate industrial activities.展开更多
文摘Low background gamma spectrometry was used to measure the radionuclides activity of <sup>238</sup>U, <sup>232</sup>Th, and <sup>235</sup>U series as well as <sup>40</sup>K and <sup>137</sup>Cs in a sediment sample. The goal of the study was to measure the <sup>238</sup>U (63.3 keV peak of <sup>234</sup>Th;1001 keV peak of <sup>234m</sup>Pa) and <sup>235</sup>U (143.76 keV, 163.33 keV, and 205.31 keV peaks) activity by low background gamma spectrometry in sediment sample. <sup>235</sup>U activity in environmental samples is difficult to accurately measure by gamma spectrometry due to its low abundance in nature and low gamma line intensities at 143.76 keV, 163.33 keV, and 205.31 keV. We have shown that by using low background gamma spectrometry, it is possible to accurately measure the <sup>235</sup>U activity in sediment samples. The <sup>235</sup>U activity was measured without using the major peak of 185.7 keV (I<sub>γ</sub> = 57.2%) which requires interference correction from 186.21 keV of <sup>226</sup>Ra. <sup>226</sup>Ra activity was determined by measuring <sup>222</sup>Rn daughters (<sup>214</sup>Pb and <sup>214</sup>Bi). The precision and accuracy of the gamma activity measurement in the sediment sample were verified by using the HPGe detectors with Certified Reference Material (CRM) Irish Sea Sediment (IAEA-385). The results obtained for the 63.33 keV energy line of <sup>234</sup>Th are compared with the 1001 keV energy line of <sup>234m</sup>Pa. The values of <sup>238</sup>U and <sup>235</sup>U activities, as well as <sup>40</sup>K, <sup>137</sup>Cs, and <sup>226</sup>Ra, agreed with the certificate values of CRM. The results show that the <sup>238</sup>U is in equilibrium with its daughters (<sup>234</sup>Th, <sup>234m</sup>Pa, and <sup>210</sup>Pb). <sup>232</sup>Th is also in equilibrium with its daughters (<sup>228</sup>Ra, <sup>212</sup>Pb, <sup>212</sup>Bi and <sup>208</sup>Tl). <sup>235</sup>U/<sup>238</sup>U activity ratio of 0.046 ± 0.007 in the sediment is constant in nature but fluctuates due to geological processes. A value of 0.055 ± 0.008 was found in our sediment sample.
文摘Mexico is one of the largest producers of nopal (Opuntiaficus indica). This "vegetable" is consumed on a daily basis by the Mexican population, being a source of food nutrients. Among its benefits, it is considered the content of potassium, which is essential for human life and health. In this study, it analyzes the content of potassium of the Mexican cactus (Opuntiaficus indica) grown in 5 different regions in the Mexican Basin, where 67% of the nopal is produced for human consumption. The used methodology is gamma spectrometry with Hyperpure Germanium detector (HPGe) and Multichannel Analyzer (MCA) with Maestro~ software. The results show interesting aspects on the concentration of potassium in the nopal. This concentration will primarily depend on: (a) the geological characteristics of the location where the nopal was grows; (b) that potassium concentrations may vary substantially from a region to another, with the same species of nopal as a reference and (c) that this concentration may also vary from one growing season to another.
文摘Gamma-ray spectroscopy based on a 100% efficiency hyper-pure germanium detector was used to evaluate the activity concentrations of <sup>226</sup>Ra, <sup>232</sup>Th, and <sup>40</sup>K natural radionuclides in sedimentary, conglomerate, igneous and sedi-ments rock samples collected from four different locations in Eastern desert in Egypt. The obtained activity concentrations are used to evaluate the radi-ological hazards indices, absorbed dose rate, annual effective dose equivalent in air, radium equivalent, external and internal hazard index, radiation level index, annual gonadal dose equivalent, excess lifetime cancer risk and expo-sure rate. The results show that 1) the absorbed dose rate depends on the rock type, 2) the annual effective dose equivalent in air in 71% of sample below 20 mSvy<sup>-1</sup> (permissible limit for workers), 3) the conglomerate rocks show low radioactivity level, 4) sedimentary rocks are rich in radium while igneous rocks are rich in thorium and the sediments rocks are rich in both radium and thorium.
文摘In this study, sixteen soil and vegetable samples from Tafila district were collected and analyzed from eight locations. Measurements of specific activity of natural gamma emitter radionuclides, 23SU and 235U, in these samples using gamma spectrometry, with the help of Genie 2000 software. Measurements were used to calculate the soil-vegetable transfer factor, and then the external radiation dose and internal radiation dose due to radioactivity of the ingested food. The specific activity of238U and 235U in soil were found to vary from (in Bq/kg): 26-575 and 1.4-35.5, respectively. The specific activity of 238U and 235U in vegetables were found to vary from (in Bq/kg): 0.019 to 0.632 and 0.0013-0.0375, respectively. The calculated transfer factor of Z3SU and Z35U range from 5.9 × 10^-4to 14.6 × 10^-4 for 238U and 4.9 × 10^-4 to 16.1 × 10^-4 for 235U. External absorbed dose rates were calculated to be in the range from 12.42 to 266.00 nGy/h. The annual effective dose was found to vary from 28.94 to 619.78 μSv/y. The annual internal effective dose due to 23SU and 23SU for fresh weights ofvegetablesl were found to vary from 0.9 × 10^-3 to 35.1 × 10^-3 μSv/y for 238U and 0.61 × 10^-4 to 17.62 × 10^-4 μSv/y for 235U.
文摘Twenty-eight environmental samples (eight well water, sixteen granitic rocks and four soils) were collected from different parts of Adham governorate (Adham, Haqal and Al-Jaizah), to assess the radiological hazard and cancer risk from different perspectives. Adham is situated in a valley between two granitic mountain chains, where much of water supply for drinking, house use and irrigation comes from wells collecting water rains. The activity concentrations of naturally occurring <sup>40</sup>K, <sup>226</sup>Ra and <sup>232</sup>Th and radionuclides were measured by gamma-ray spectrometry for all samples using RGK-1, RGU-1 and RGTh-1, IAEA reference standards issued by the International Atomic Energy Agency, for detector efficiency calibration. The measured values were utilized to evaluate the internal and external exposures both outdoors and indoors. Different standard room models were adopted for this respect to evaluate the indoor gamma-rays exposure from construction materials as well as internal exposure to radon gas emanating from them. Radon concentration indoors, exceeded the upper reference level in dwellings set at 300 Bq/m<sup>3</sup> by the world health organization, in many scenarios. The mean value of the total excess lifetime cancer risk (due to external exposure from gamma-rays) was 2.29 × 10<sup>-3</sup>, above the world average value of 1.45 × 10<sup>-3</sup>. Furthermore, the measured radon concentrations in all water samples exceeded the EPA (Environmental Protection Agency) 11.1 Bq·L<sup>-1</sup> standard for drinking water, ranging from 12 to 38 Bq·L<sup>-1</sup> with a mean value of 27 Bq·L<sup>-1</sup>. The total annual effective dose (due to inhalation and ingestion) from radon in water, ranged from 58 to 192 μSv/y (for adults) exceeding the international permissible limit of 100 μSv/y, in seven out of eight samples. According to obtained results, the internal exposure from radon in directly used water from wells, might be the major reason of any suspected radiological health hazard especially in Haqal. The second reason might be the internal exposure from indoor radon gas inhalation in poorly ventilated dwellings.
文摘The Uranium-238 (<sup>238</sup>U), Thorium-232 (<sup>232</sup>Th) families and Potassium-40 (<sup>40</sup>K) are of terrestrial origin and contribute generally to an individual’s external exposure through our presence in this environment. They also contribute to the internal exposure through the ingestion of products and beverages such as water that are close to the earth. The aim of this work is to determine the committed effective dose or Total Indicative Dose (TID) due to gamma radioactivity of the borehole water from the Nord Riviera (NR) well field operated by the Côte d’Ivoire Water Distribution Company (SODECI) for the supply of drinking water to part of the population of Abidjan. In addition, the populations, with their habits, could use these borehole waters directly as drinking water. To this end, water samples from the seven (07) functional boreholes were collected and analyzed on a gamma spectrometry chain, equipped with an HPGe detector in the laboratory of the Radiation Protection Institute (RPI) of the GHANA Atomic Energy Commission (GAEC). The results of the specific activities of <sup>238</sup>U, <sup>232</sup>Th and <sup>40</sup>K obtained were transcribed into TID. As the natural radioactivity of the borehole water is high [1], the TIDs calculated from the activity results of the natural radionuclides<sup>238</sup>U, <sup>232</sup>Th, and <sup>40</sup>K vary for the seven boreholes from 0.150 to 0.166 mSv/yr with an average of 0.161 ± 0.034 mSv/yr. The TID of the control tower, where the borehole water is mixed and treated for household use, is equal to 0.136 ± 0.03 mSv/yr. The TIDs obtained are therefore all slightly greater than the WHO reference dose value of 0.1 mSv/yr. But all remain below the UNSCEAR reference dose of 0.29 mSv/yr.
文摘Coal is the main energy source for electricity generation in the world. In Morocco, 37% of electricity generation comes from combustion coal in thermal power plants. This combustion process generates large amounts of fly and bottom ashes. In recent years, these ashes became a great topic of interest because of their different uses and especially in construction materials. In this work, we assess radiation risks due to natural radioactivity in samples of fly and bottom ashes collected from JLEC (Jorf Lasfar Energy Company) thermal power plant, and different analyses are performed through two nuclear techniques such as gamma spectrometry and alpha dosimetry based on the use of LR115 films detectors. Our analysis shows that <sup>226</sup>Ra activities and <sup>232</sup>Th in both ash samples are well above the permissible activity. The values of the external risk index (H<sub>ex</sub>) and internal one (H<sub>in</sub>) for these ashes are below unity, with the exception of 1.28 in fly ash for H<sub>in</sub>. The obtained values for the equivalent radium Ra<sub>eq</sub> and annual effective doses Ėin fly and bottom ashes are 324 Bq/kg and 210 Bq/kg, and 0.18 mSv/y and 0.11 mSv/y, respectively. The surface radon exhalation rates for the samples of fly and bottom ashes are 276 mBq⋅m<sup>-2</sup>⋅h<sup>-1</sup> and 381 mBq⋅m<sup>-2</sup>⋅h<sup>-1</sup>, respectively. Based on these results, we have shown that fly ash and bottom one from thermal power plant JLEC didn’t have, in any case, a health risk to the public so it can be effectively used in various construction activities.
文摘Soils and other solid wastes from industrial areas of Nasirabad, Chattogram are usually dumped or used for land development. Information about the radioactivity level presented on these soil and wastes enables one to assess any possible radiological hazard to humankind by the use of such materials. A total of 37 (31 soils and 6 solid waste) samples near from different types of industries along four kilometre range were collected. The presence and activity concentrations of naturally occurred radioactive materials (NORM) and anthropogenic radionuclides in the samples were estimated using HPGe detector of 40% relative efficiency. The activity concentration of <sup>226</sup>Ra, <sup>232</sup>Th and <sup>40</sup>K were found to be ranging from 8 ± 2 to 131 ± 18.33 with an average of 21 Bq<span style="white-space:nowrap;">·</span>kg<sup>-1</sup>, 10 ± 2.69 to 133 ± 15.96 with an average of 40 Bq<span style="white-space:nowrap;">·</span>kg<sup>-1</sup> and 81 ± 22.68 to 930 ± 260.40 with an average of 449 Bq<span style="white-space:nowrap;">·</span>kg<sup>-1</sup> respectively. Besides this, some hazard indices like, the radium equivalent activity (<em>Ra<sub>eq</sub></em>), external hazard index (<em>H<sub>ex</sub></em>), internal hazard index (<em>Hi<sub>n</sub></em>), and the activity concentration index (<em>I</em><sub>y</sub>) were calculated to assess the radiation hazard in this region. The averages of calculated hazard indices were within the normal limits, except the activity concentration index, which shows elevated values. The outcomes of this study could serve as important baseline radiological data for future epidemiological studies and environmental monitoring initiatives in the study area.
文摘The assessment of radiological hazard due to external and internal indoor exposure was investigated for 26 raw granites collected from different granite quarries in Ranyah (KSA). The activity concentrations of <sup>226</sup>Ra, <sup>232</sup>Th and <sup>40</sup>K were measured by high-resolution gamma spectrometry. Four granites were classified as “anomalous” due to their relatively high radioactivity. The averages and ranges of their activity concentrations were 667 (305 - 1120), 320 (161 - 491) and 586 (282 - 893) Bq·kg<sup>-1</sup>, respectively. The corresponding ones for all remaining 22 granites were 45 (18 - 77), 39 (16 - 73) and 1178 (954 - 1531) Bq·kg<sup>-</sup><sup>1</sup>, respectively. In accordance with new European Basic Safety Standards (BSS) directives requiring a uniform reference level for indoor external exposure to gamma rays of 1 mSv·y<sup>-</sup><sup>1</sup>, all 22 granites may be used as bulk or ornamental building materials without any restrictions. Three anomalous granites should be subjected to control to be used as bulk materials. One anomalous granite was categorized as hazardous having an activity concentration index higher than 6. All four anomalous granites exceeded the level of newly adopted reference level of 300 Bq·m<sup>-</sup><sup>3</sup> for radon indoor exposure in case of poor ventilation. Two of them exceeded even for adequate ventilation. ·
文摘This study assesses radiation levels in soil, water and air in the Norochcholai,<span> </span><span>an area in Sri Lanka closest to the Kundankulam nuclear power plant, India which is situated in the North Western coast. This is important for monitoring radiation hazards </span><span><span><span style="font-family:;" "="">and</span></span></span><span><span><span style="font-family:;" "=""> will be useful in case of a nuclear accident. Superficial soil and water samples from 23 locations were analyzed by Gamma spectrometry using<span style="color:red;"> </span>HPGe detector. The activity concentrations of Th232, K40, Ra226 and Pb210 in the soil were 56.0</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq<span style="white-space:normal;">·</span>kg</span></span></span><span><span><span><span><sup><span style="font-family:;" "=""><span style="font-size:10px;">-</span>1</span></sup></span></span></span></span><span></span><span></span><span><span><span style="font-family:;" "="">, 96.0</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq</span></span></span>·<span><span><span style="font-family:;" "="">kg</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "="">, 24.0</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq<span style="white-space:normal;">·</span>kg</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "=""> and 27.0</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq<span style="white-space:normal;">·</span>kg</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "=""> respectively. Dose rate at 1</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">m height w</span></span></span><span><span><span style="font-family:;" "="">as</span></span></span><span><span><span style="font-family:;" "=""> recorded using a survey meter</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">(Automess 6150AD). Median dose rate was 0.098</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">μSv<span style="white-space:normal;">·</span>h</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "="">. The median gamma ray absorbed dose rate w</span></span></span><span><span><span style="font-family:;" "="">as</span></span></span><span><span><span style="font-family:;" "=""> 51.2 nGy<span style="white-space:normal;">·</span>h</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "="">,</span></span></span><span><span><span style="font-family:;" "=""> which is lower than the global average of 57 nGy<span style="white-space:normal;">·</span>h</span></span></span><span><span><sup><span style="font-family:;" "=""><span><span style="font-size:10px;">-</span>1</span></span></sup></span></span><span><span><span style="font-family:;" "="">. Radium equivalent activity</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">(Raeq) ranged from 30.3</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq/Kg -</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">458.3</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq/Kg and only one sample recorded the Raeq ></span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">370</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">Bq/Kg as safe to be used in building materials. External hazardous indices of all the samples w</span></span></span><span><span><span style="font-family:;" "="">ere</span></span></span><span><span><span style="font-family:;" "=""> below 1 a</span></span></span><span><span><span style="font-family:;" "="">nd the mean annual effective dose was within the safe limit of 1</span></span></span><span><span><span style="font-family:;" "=""> </span></span></span><span><span><span style="font-family:;" "="">mSv/y. The health risk of exposure to terrestrial radiation from the soil in the area is minimal. These data could be used as baseline for radiation assessment.</span></span></span>
文摘Knowledge of radioactivity present in polishing materials enables one to assess any possible radiological risks to human health. In this work, the radioactivity due to the presence of <sup>226</sup>Ra, <sup>232</sup>Th, <sup>40</sup>K, and <sup>37</sup>Cs has been measured in polishing materials con-sumed in Saudi Arabia using gamma spectrometry with HPGe. The activity concentra-tions of <sup>226</sup>Ra, <sup>232</sup>Th, <sup>40</sup>K and <sup>137</sup>Cs ranged from 13.61 ± 0.005 to 0.60 ± 0.002, 18.43 ± 0.003 to 0.78 ± 0.001, 342.59 ± 0.009 to 2.47 ± 0.001 and 1.47 ± 0.001 to 0.55 ± 0.001 Bq/l, respectively. For <sup>226</sup>Ra and <sup>40</sup>K, the highest values are measured in stainless steel polisher. The highest values also measured in metal polisher (copper-chrome) and disinfectant cleaner and polisher sample for <sup>232</sup>Th and <sup>137</sup>Cs. Radium equivalent activ-ity due to the natural radioactivity of the investigated samples ranged from 51.37 to 1.24 Bq/l. This value is less than the recommended values in the established standards. The evaluated data were compared with the literature data. Our results indicate that no significant radiological hazards arise from using investigated samples hence quite safe to be used as polishing materials.
文摘In this work, ten medicinal and nutritional leaves samples of <em>Hibiscus sabdariffa</em> Linn imported from Mali and Burkina Faso in C<span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">ô</span></span></span>te d’Ivoire and sold on the market were collected. The analysis of these plants using High Purity Germanium detector (HPGE) gamma spectrometry showed the activity concentrations of <sup>226</sup>Ra, <sup>232</sup>Th, and <sup>40</sup>K varied respectively in the range of (1.74 - 0.11) × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>3</sup> Bq/kg, (6.72 - 0.61) × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>4</sup> Bq/kg and (4.65 - 0.54) × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>3</sup> Bq/kg1 in the leaves of <em>H. sabdariffa</em>. The Average Annual Committed Effective Dose (AACED) values from leaves this plant varied from 251.492 × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>6</sup> to 68.133 × 10<sup><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;"><span style="white-space:nowrap;">−</span></span></span></span>6</sup> mSv/y. These values found are below 0.30 mSv/y, the world average value for an individual. These results show that there is no radiological risk in consuming “bissap” leaves.
文摘Objective To investigate the specific activities of gamma radionuclides in the soils around high energy accelerators,and to analyze the influence of rays emitted by nuclides with characteristic peaks at similar energy points on nuclide measurement results,in order to provide reference for the accurate identification of radionuclides.Methods GR5021 high-purity germanium gamma spectroscopy system was used to measure the specific activities of gamma-emitting radionuclides 226Ra,232Th,238U,40K and artificial radionuclides 54Mn,52Mn,7Be,22Na,59Fe,95Zr in six soil samples around three kinds of high energy accelerators,and the theoretical counts of the characteristic peak of 835.7keV were compared with the measured counts of the characteristic peak of 54Mn.Results The specific activity ranges of gamma-emitting radionuclides 226Ra,232Th,238U and 40K in the soils around three kinds of high energy accelerators were 55.5–171,34.9–99.9,21.9–79.3 and 247–680 Bq/kg,respectively.The specific activities of artificial radionuclides 52Mn,7Be,22Na,59Fe and 95Zr were basically lower than the minimum detection limit.A characteristic peak was found at the energy point of 835.7keV in six soil samples,and the corresponding total absorption peak counts were from 228Ac of 232Thdecay daughter.Conclusions The specific activities of gamma-emitting radionuclides were at the normal natural background levels.The specific activities of artificial radionuclides were basically lower than the minimum detection limits.For 232Th,when its specific activity is above 40 Bq/kg,characteristic peak of its decay daughter 228Ac could be misjudged as characteristic peak of 54Mn.
基金The authors wish to express their deep appreciation and gratitude to the IAEA for awarding the fellowship,without which this work would have been impossibleand the Director General of the National Radiation Protection Agency of Cameroon,Dr.Augustin SIMO for the laboratory support.The authors also appreciate the community of Hahotoé-Kpogaméfor the understanding during sampling period.They also wish to thank Dr.Michel WARNAU,Programme Management Officer for IAEA to Togo for his understanding and availability to this work.We also wish to address special thanks to Col.MANZI Pidalatan,National Liaison Officer of Togo and project coordinator of IAEA TC Project Number:TOG/0/002 provided in granting access to the facilities to successfully complete this study.
文摘Introduction Because of the increasing use of phosphate in industries worldwide,especially in Togo,it is interesting to investigate the potential radioactivity exposure of phosphate ores,especially in the one being exploring in Togo nowadays.Material and methods The contents of natural radionuclides(40K,226Ra,232Th,235U and 238U)were assessed in phosphate soil samples from Kpogamé,Dagbati and Kpéméin the maritime region of Togo by using gamma spectrometry-based Broad Energy Germanium detector(BEGe6530).Since no study was made prior to the exploitation,the samples from the control area of Anfoin-Kpota far away from the three others were considered as reference.Results and discussion The results are discussed and compared with the data from other countries.The activity concentration of 40K,226Ra,232Th,235U and 238U are between(59.45 and 129.99),(20.19 and 779.93),(16.81 and 121.42),(2.26 and 52.03)and(16.66 and 841.14)Bq kg^(−1),respectively.The values obtained shows that the exploitation sites(Dagbati and Kpogamé)and treatment site(Kpémé)have a very high level of radioactivity than the control area(Anfoin-Kpota).The Kpogaméand Dagbati exploitation and Kpéméwaste discharging phosphate deposit sites were found to have higher activity concentration than many others exploited phosphate sedimentary deposits around the world.The average annual effective dose of the above studied sites is 0.36,0.24 and 0.48 mSv year−1,respectively.The value related to the discharge waste site is about 2%of the 1.0 mSv year−1 recommended by the International Commission on Radiological Protection as the maximum annual dose to the public.Conclusions The obtained result of both radioactivity and radiological level in the studied areas will be considered as a pre-operational baseline to estimate the possible radiological impacts due to mining and processing phosphate industrial activities.