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Journal articles on the topic 'Environmental aspects of Radioactivity'

Author: Grafiati

Published: 4 June 2021

Last updated: 1 February 2022

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1

Pontikes, Y., I. Vangelatos, Dimitri Boufounos, Dimitris Fafoutis, and G. N. Angelopoulus. "Environmental Aspects on the Use of Bayer's Process Bauxite Residue in the Production of Ceramics." Advances in Science and Technology 45 (October 2006): 2176–81. http://dx.doi.org/10.4028/www.scientific.net/ast.45.2176.

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Bauxite Residue (BR) is the main waste generated during the alumina-producing Bayer process. With the aim to utilize BR in the production of traditional ceramics, the potential impact such a use might have on the leaching behaviour and radioactivity levels of the final products was investigated. Leaching behaviour of Cr, Ni and V on calcined BR was studied according to the maximal availability test, NEN 7341. Firing atmosphere, firing temperature and soaking time were the investigated parameters. Results demonstrate that the soluble fraction of Cr is higher for oxidizing atmosphere whereas the soluble fraction of V and Ni increases for inert and reducing atmosphere, respectively. For assessing radioactivity, the activity concentrations of 226Ra, 40K, and 232Th were determined by means of gamma ray spectroscopy. For an excess gamma dose less than 1mSv/a, the maximum quantity of BR that can be introduced replacing the raw materials ranges from 14wt.% up to 100wt.%, depending on the type of product and the extent of use in the dwelling.

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2

ZHANG, YUANXUN, DEYI LI, YINSONG WANG, WAIGUO SHEN, MIN ZHI, GUILIN ZHANG, YAN LI, ERHKANG LIN, YUEHCHUNG YU, and CHANGWAN WANG. "MONITORING RIVER WATER AND SEDIMENT SAMPLES BY BOTH PIXE ANALYSIS AND RADIOACTIVITY DETERMINATION." International Journal of PIXE 12, no. 03n04 (January 2002): 199–208. http://dx.doi.org/10.1142/s0129083502000317.

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In cooperation with the Shanghai Environmental Specimen Bank (SESB) research project and in support of the Shanghai government's comprehensive plan to harness the Suzhou River, we collected water and sediment samples in the every spring season since 1998. The elemental analysis of sediment and water samples was performed by the PIXE technique using the 3 × 2 MeV NEC Tandem accelerator at the Taipei Institute of Physics. The characterization of á and â radioactive levels for water and sediment samples was performed using BH1216, low-background, radioactivity instrument at the Shanghai Institute of Nuclear Research. PIXE results showed that the content of Cl , K , Ca , Cr , Mn , Fe , Zn and Pb in river water gradually decreased with the rising tide. At high tide, their concentrations were minimum, and then once again increased toward the ebb tide. The analysis also demonstrated that the radioactivity of water samples had been gradually decreasing year by year. It was found that the decreasing rate of á radioactivity was a little quicker than that of â radioactivity. Further aspects of environmental data evaluation and assessment are also discussed in detail.

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3

Matsuoka, N., T. Umata, M. Okamura, N. Shiraishi, N. Momoshima, and Y. Takashima. "Determination of technetium-99 from the aspect of environmental radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 140, no. 1 (May 1990): 57–73. http://dx.doi.org/10.1007/bf02037364.

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4

Radenkovic, Mirjana, Alshikh Masaud, Velibor Andric, and Scepan Miljanic. "Radioactivity of sand from several renowned public beaches and assessment of the corresponding environmental risks." Journal of the Serbian Chemical Society 74, no. 4 (2009): 461–70. http://dx.doi.org/10.2298/jsc0904461r.

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The radiological risk due to the presence of natural and man-made radionuclides in beach sands from several renowned seaside and riverbank public beaches was estimated in this study. The exposure levels to terrestrial radiation of the beaches were determined, as well as hazards due to human use of the analyzed sands in industry and in building constructions. Specific radionuclides concentrations in the sand samples were determined by standard gamma-spectrometry. The corresponding radiation hazards arising due to the use of sand as a building material were estimated by three different radiological hazard indices. The total absorbed gamma dose rate in the air was determined and the corresponding annual effective dose outdoors was estimated. The obtained data are relevant both from human health and environmental monitoring aspects.

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5

Mietelski, Jerzy W., and Pavel P. Povinec. "Environmental radioactivity aspects of recent nuclear accidents associated with undeclared nuclear activities and suggestion for new monitoring strategies." Journal of Environmental Radioactivity 214-215 (April 2020): 106151. http://dx.doi.org/10.1016/j.jenvrad.2019.106151.

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6

Ahijjo, Yusuf Musa, A. N. Baba-Kutigi, M. Momoh, A. M. Bayawa, and M. Hussain. "An Awareness Survey of Inhabitants Exposure to Radiological Impacts on Mines in Yauri LGA, Kebbi State, Nigeria." European Journal of Engineering Research and Science 3, no. 11 (November 6, 2018): 12–15. http://dx.doi.org/10.24018/ejers.2018.3.11.956.

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A cross-sectional survey was conducted in Yauri LGA, Kebbi State in between April, 2015 and January, 2016 in order to ascertain the level of awareness of inhabitant’s exposure to radioactivity from the mines. Yauri LGA was sampled based on its metropolitan and suburban parts that receives heavy mining activities by stratified random sampling by proportions. An interactive medium was created to sample the opinions of inhabitants around these mines through questionnaire. A total of 150 questionnaire were designed, 30 were accepted by the respondents and 22 were returned with response from the correspondents during the survey and interview to document and assessment awareness of the inhabitants. The study unveiled facts about the inhabitant’s awareness towards the environmental and health effect of indiscriminate mining activities around living places. The results shows that over 70% of the inhabitants within the suburb and metropolis concurred to the potential health consequences in their dwellings as a result of exposure to radioactivity from the mines respectively. These results indicates that the environmental and health discomfort due to indiscriminate mining activities around living places will be more significant in the near future if no immediate efforts are put in place to mimic future malady. The second aspect of this study whose results will be published in the subsequent issue involved collection of soil, water and vegetation samples in order to further assess the level of radioactive elements viz: 226Ra, 232Th and 40K occurrence in the study locality.

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7

Stepanova, Ye, I. Kolpakov, V. Vdovenko, V. Zigalo, V. Kondrashova, and O. Leonovich. "MOLECULAR GENETIC ASPECTS OF BRONCHIAL HYPERREACTIVITY IN CHILDREN – RESIDENTS OF RADIOACTIVELY CONTAMINATED AREAS." Проблеми радіаційної медицини та радіобіології = Problems of Radiation Medicine and Radiobiology 25 (2020): 531–42. http://dx.doi.org/10.33145/2304-8336-2020-25-531-542.

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Objective. to determine the relationship between polymorphisms of glutathione S-transferase gene family and bronchial hyperreactivity in children living in radioactively contaminated areas. Materials and methods. School age children-residents of radioactively contaminated areas (RCA), without clinical signs of respiratory pathology were examined. Molecular genetic studies were carried out by polymerase chain reaction (PCR) and restriction fragment length polymorphism (RFLP) for further analysis. The GSTT1, GSTM1 gene deletion polymorphism was investigated using multiplex PCR. PCR and PCR-RFLP analyses were performed in the study of the GSTP1 gene A313G polymorphism. The ventilation lung capacity was examined by the pneumotachographic method according to the analysis of «the flow–volume» loop. The pharmacologic inhalation test with bronchodilator drug, affecting the β2-adrenergic lung receptors was used to detect the early changes in the ventilation lung capacity – the bronchial hyperreactivity (latent and nonlatent bronchospasm). Results. Molecular genetic studies showed that the GSTM1 gene deletion genotype and the GSTP1 gene A313G polymorphism were found significantly more often in the subgroup of children with bronchial hyperreactivity living in RCA than in children without bronchial hyperreactivity and children of the control group. The frequency of GSTT1 deletion polymorphism did not have a statistically significant difference in all subgroups. Conclusions. The GSTM1 gene deletion polymorphism and the GSTP1 gene A313G genotype may be a risk factor for developing bronchial hyperreactivity in children living under adverse environmental conditions, including radioactively contaminated areas. Key words: children, radioactively contaminated areas, bronchial hyperreactivity, glutathione-S-transferase gene polymorphisms.

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8

Naito, Wataru, Motoki Uesaka, Yujiro Kuroda, Takahiko Kono, Akihiro Sakoda, and Hiroko Yoshida. "Examples of practical activities related to public understanding of radiation risk following the Fukushima nuclear accident." Radioprotection 55, no. 4 (October 2020): 297–307. http://dx.doi.org/10.1051/radiopro/2020086.

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After the Fukushima nuclear accident in Japan, a number of practical activities related to public understanding (PU) of radiation risks were implemented inside and outside Fukushima Prefecture. The various noteworthy approaches and strategies behind those practical activities have not been organized and made explicit thus far. In this study, we have organized the noteworthy practical activities related to PU of radiation risks following the Fukushima nuclear accident, and discussed them mainly from the standpoints of communication strategies and approaches. As several examples demonstrate, efforts to contextualize and localize radiation risk in various forms were observed during post-accident recovery in Fukushima, and these efforts were confirmed, through actual experiences, to be an important component of effective PU activities of radiation risks. Community-based or citizen science approaches, such as having affected residents or citizens to measure radioactivity, have contributed to the PU of radiological situations, but some challenges, such as ethical aspects and the handling of uncertainty, have also been revealed. In the era of information and communications technology, a number of citizens, experts, and agencies have made social media a popular platform for disseminating radiation risk messages to the public and have demonstrated that social media can play an important role in providing radiological risk information. The knowledge and lessons learned from the practical activities discussed in this study can be useful in enhancing PU of risks not only radiation but also other stressors such as toxic chemicals, preparing future disasters and supporting risk communication plans during recovery periods after disasters.

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9

Slavata, Branislava, Gordana Vitorovic, and Slobodan Dzonic. "Radiation-hygiene control of imported foodstuffs and cattle feed." Veterinarski glasnik 56, no. 3-4 (2002): 237–45. http://dx.doi.org/10.2298/vetgl0204237s.

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The increasingly frequent use of nuclear energy in peacetime, experimental nuclear and thermo-nuclear explosions, as well as accidents in nuclear plants lead to an increased and unequal distribution of radioactive substances in the environment. Mankind is in this way threatened not only by environmental irradiation, but also by consuming contaminated food and water which contain radionuclides whose concentrations are above the level of natural radioactivity. From the aspect of the veterinary profession, the most important task is to organize the protection of domestic animals and their products from radioactive contamination. This work presents the results obtained by measurements of the activity level of 137Cs in products of animal origin and cattle feed, in samples obtained from border crossings in Yugoslavia and partly in Macedonia during the period from 1990 until 1999. Examined import samples were taken from cheese, prok, and corn and the activity level of 137Cs was within the permitted legal levels - less than 1 Bq/kg. However, powdered milk was found to contain an activity level of 137Cs from 1,22-7,27 Bq/kg, and saltwater fish from 1,10-3,30 Bq/kg, so that these products could not be released for sale under the Official Gazette of the FRY, Number 53/91.

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10

Cheng, E. T. "Radioactivity aspects of fusion reactors." Fusion Engineering and Design 10 (January 1989): 231–42. http://dx.doi.org/10.1016/0920-3796(89)90058-6.

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11

Peterson, Harold T. "Environmental radioactivity." Journal of Environmental Radioactivity 5, no. 6 (January 1987): 480–81. http://dx.doi.org/10.1016/0265-931x(87)90022-1.

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12

Eisenbud, M., and A. S. Paschoa. "Environmental radioactivity." Nuclear Instruments and Methods in Physics Research Section A: Accelerators, Spectrometers, Detectors and Associated Equipment 280, no. 2-3 (August 1989): 470–82. http://dx.doi.org/10.1016/0168-9002(89)90953-4.

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13

Silva, R. J. "Environmental radioactivity." Journal of Radioanalytical and Nuclear Chemistry 264, no. 2 (May 2005): 333–36. http://dx.doi.org/10.1007/s10967-005-0717-6.

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14

Bayer, A. "Radiation protection aspects in natural radioactivity." Kerntechnik 73, no. 3 (May 2008): 85. http://dx.doi.org/10.3139/124.080302.

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15

Bogdanov, R. V., A. G. Krivitskii, Yu S. Polekhovskii, and N. V. Vinogradova. "Radioactivity of vanadium ore: Radioecological aspects." Radiochemistry 48, no. 3 (May 2006): 307–14. http://dx.doi.org/10.1134/s1066362206030180.

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16

NÉMETH, Csaba, and Shinji TOKONAMI. "Environmental Radioactivity in Hungary." Japanese Journal of Health Physics 39, no. 2 (2004): 113–18. http://dx.doi.org/10.5453/jhps.39.113.

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17

Adriano, D. C. "Environmental Radioactivity, Third Edition." Journal of Environmental Quality 17, no. 1 (January 1988): 173. http://dx.doi.org/10.2134/jeq1988.00472425001700010039x.

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18

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 111, no. 2 (April 1987): 487–502. http://dx.doi.org/10.1007/bf02072880.

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19

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 170, no. 1 (April 1993): 281–91. http://dx.doi.org/10.1007/bf02134599.

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20

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 100, no. 2 (August 1986): 389–408. http://dx.doi.org/10.1007/bf02037245.

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21

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 181, no. 1 (June 1994): 231–50. http://dx.doi.org/10.1007/bf02037562.

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22

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 109, no. 2 (February 1987): 507–19. http://dx.doi.org/10.1007/bf02037891.

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23

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 158, no. 1 (April 1992): 215–37. http://dx.doi.org/10.1007/bf02034788.

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24

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 91, no. 1 (August 1985): 227–49. http://dx.doi.org/10.1007/bf02036331.

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25

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 207, no. 1 (July 1996): 215–32. http://dx.doi.org/10.1007/bf02036541.

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26

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 109, no. 1 (January 1987): 247–60. http://dx.doi.org/10.1007/bf02117541.

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27

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 98, no. 1 (March 1986): 195–218. http://dx.doi.org/10.1007/bf02060445.

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28

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 204, no. 1 (March 1996): 213–28. http://dx.doi.org/10.1007/bf02060882.

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29

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 177, no. 2 (January 1994): 425–37. http://dx.doi.org/10.1007/bf02061139.

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30

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry 238, no. 1-2 (December 1998): 227–35. http://dx.doi.org/10.1007/bf02385385.

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31

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry 227, no. 1-2 (January 1998): 195–205. http://dx.doi.org/10.1007/bf02386461.

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32

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry 232, no. 1-2 (June 1998): 265–76. http://dx.doi.org/10.1007/bf02383755.

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33

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry 241, no. 3 (September 1999): 683–93. http://dx.doi.org/10.1007/bf02347235.

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34

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry 241, no. 1 (July 1999): 245–55. http://dx.doi.org/10.1007/bf02347324.

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35

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry 242, no. 3 (December 1999): 829–36. http://dx.doi.org/10.1007/bf02347405.

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36

Amiro, B. D. "Frontiers of environmental radioactivity." Journal of Radioanalytical and Nuclear Chemistry 239, no. 1 (January 1999): 45–52. http://dx.doi.org/10.1007/bf02349531.

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37

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry 218, no. 1 (April 1997): 135–45. http://dx.doi.org/10.1007/bf02033991.

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38

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 210, no. 1 (October 1996): 237–54. http://dx.doi.org/10.1007/bf02055423.

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39

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 140, no. 2 (June 1990): 425–40. http://dx.doi.org/10.1007/bf02039516.

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40

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 133, no. 1 (September 1989): 167–83. http://dx.doi.org/10.1007/bf02039973.

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41

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry 219, no. 1 (May 1997): 139–48. http://dx.doi.org/10.1007/bf02040283.

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42

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 147, no. 2 (February 1991): 385–401. http://dx.doi.org/10.1007/bf02040388.

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43

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 130, no. 2 (April 1989): 461–76. http://dx.doi.org/10.1007/bf02041365.

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44

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 125, no. 2 (December 1988): 493–512. http://dx.doi.org/10.1007/bf02041707.

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45

Bujdosó, E. "Environmental radiochemistry and radioactivity." Journal of Radioanalytical and Nuclear Chemistry Articles 172, no. 2 (August 1993): 395–406. http://dx.doi.org/10.1007/bf02041860.

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46

Trabalka, John R. "Radioecology: Lectures in environmental radioactivity." Journal of Environmental Radioactivity 31, no. 2 (January 1996): 217–18. http://dx.doi.org/10.1016/s0265-931x(96)90005-3.

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47

Larkin, James, Henk Coetzee, Shaun Guy, and John Watterson. "Environmental radioactivity in South Africa." Radiation Physics and Chemistry 71, no. 3-4 (October 2004): 795–96. http://dx.doi.org/10.1016/j.radphyschem.2004.04.096.

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48

Strand, Per. "Environmental radioactivity in the arctic." Science of The Total Environment 202, no. 1-3 (August 1997): 1–3. http://dx.doi.org/10.1016/s0048-9697(97)00100-9.

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49

Boyer, Michael C. "Environmental radioactivity and the weather." Physics Teacher 33, no. 9 (December 1995): 554–55. http://dx.doi.org/10.1119/1.2344300.

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50

Riland, Carson A. "Environmental radioactivity, temperature, and precipitation." Physics Teacher 34, no. 4 (April 1996): 234–35. http://dx.doi.org/10.1119/1.2344416.

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