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General approach to dose reconstruction in the population exposed as a result of the release of radioactive wastes into the Techa river
Massive releases of fission products from the plutonium production facility ‘Mayak’ resulted in the years 1949–1956 in the contamination of the river Techa and its flood lands. This led to the exposure of the population in many riverside villages due to external γ-rays and due to the incorporation o...
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Published in: | The Science of the total environment 1994-03, Vol.142 (1), p.49-61 |
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creator | Degteva, Marina O. Kozheurov, Vyacheslav P. Vorobiova, Marina I. |
description | Massive releases of fission products from the plutonium production facility ‘Mayak’ resulted in the years 1949–1956 in the contamination of the river Techa and its flood lands. This led to the exposure of the population in many riverside villages due to external γ-rays and due to the incorporation of radionuclides, primarily Sr-90. The exposure situation is described and the reconstruction of doses due to external and due to internal radioactivity is explained. The internal dosimetry is based on large scale measurements of Sr-90 β-rays on the surface of teeth that were begun in 1960, and on whole-body measurements of Sr-90 that were begun in 1974. The details of the analyses are presented in Part 2 of the present report. Average doses due to the external and the internal exposure are given for the residents of the different villages along the river Techa. In the total population of about 28 000 persons that were assessed, the medium dose to the red bone marrow was about 0.25 Gy and the mean dose about 0.4 Gy. In about 5% of the individuals the dose to the red bone marrow was estimated to be in excess of 1 Gy. |
doi_str_mv | 10.1016/0048-9697(94)90073-6 |
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This led to the exposure of the population in many riverside villages due to external γ-rays and due to the incorporation of radionuclides, primarily Sr-90. The exposure situation is described and the reconstruction of doses due to external and due to internal radioactivity is explained. The internal dosimetry is based on large scale measurements of Sr-90 β-rays on the surface of teeth that were begun in 1960, and on whole-body measurements of Sr-90 that were begun in 1974. The details of the analyses are presented in Part 2 of the present report. Average doses due to the external and the internal exposure are given for the residents of the different villages along the river Techa. In the total population of about 28 000 persons that were assessed, the medium dose to the red bone marrow was about 0.25 Gy and the mean dose about 0.4 Gy. In about 5% of the individuals the dose to the red bone marrow was estimated to be in excess of 1 Gy.</description><identifier>ISSN: 0048-9697</identifier><identifier>EISSN: 1879-1026</identifier><identifier>DOI: 10.1016/0048-9697(94)90073-6</identifier><identifier>PMID: 8178136</identifier><identifier>CODEN: STENDL</identifier><language>eng</language><publisher>Shannon: Elsevier B.V</publisher><subject>Adolescent ; Adult ; Age Factors ; Body Burden ; Dental Enamel - metabolism ; Dosimetry ; Environmental Exposure - analysis ; External exposure ; Fresh Water ; Freshwater ; Humans ; Internal exposure ; Radioactive contamination ; Russia ; Strontium ; Strontium Radioisotopes - analysis ; Strontium Radioisotopes - pharmacokinetics ; Techa population ; Tissue Distribution ; Water Pollutants, Radioactive - analysis ; Water Pollutants, Radioactive - pharmacokinetics</subject><ispartof>The Science of the total environment, 1994-03, Vol.142 (1), p.49-61</ispartof><rights>1994</rights><rights>1994 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c510t-343afb7264b4d92853f440290859bd05885c7e91a547614e921416800679372c3</citedby><cites>FETCH-LOGICAL-c510t-343afb7264b4d92853f440290859bd05885c7e91a547614e921416800679372c3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.sciencedirect.com/science/article/pii/0048969794900736$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,780,784,3481,27923,27924,45992</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=4102860$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/8178136$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Degteva, Marina O.</creatorcontrib><creatorcontrib>Kozheurov, Vyacheslav P.</creatorcontrib><creatorcontrib>Vorobiova, Marina I.</creatorcontrib><title>General approach to dose reconstruction in the population exposed as a result of the release of radioactive wastes into the Techa river</title><title>The Science of the total environment</title><addtitle>Sci Total Environ</addtitle><description>Massive releases of fission products from the plutonium production facility ‘Mayak’ resulted in the years 1949–1956 in the contamination of the river Techa and its flood lands. This led to the exposure of the population in many riverside villages due to external γ-rays and due to the incorporation of radionuclides, primarily Sr-90. The exposure situation is described and the reconstruction of doses due to external and due to internal radioactivity is explained. The internal dosimetry is based on large scale measurements of Sr-90 β-rays on the surface of teeth that were begun in 1960, and on whole-body measurements of Sr-90 that were begun in 1974. The details of the analyses are presented in Part 2 of the present report. Average doses due to the external and the internal exposure are given for the residents of the different villages along the river Techa. In the total population of about 28 000 persons that were assessed, the medium dose to the red bone marrow was about 0.25 Gy and the mean dose about 0.4 Gy. In about 5% of the individuals the dose to the red bone marrow was estimated to be in excess of 1 Gy.</description><subject>Adolescent</subject><subject>Adult</subject><subject>Age Factors</subject><subject>Body Burden</subject><subject>Dental Enamel - metabolism</subject><subject>Dosimetry</subject><subject>Environmental Exposure - analysis</subject><subject>External exposure</subject><subject>Fresh Water</subject><subject>Freshwater</subject><subject>Humans</subject><subject>Internal exposure</subject><subject>Radioactive contamination</subject><subject>Russia</subject><subject>Strontium</subject><subject>Strontium Radioisotopes - analysis</subject><subject>Strontium Radioisotopes - pharmacokinetics</subject><subject>Techa population</subject><subject>Tissue Distribution</subject><subject>Water Pollutants, Radioactive - analysis</subject><subject>Water Pollutants, Radioactive - pharmacokinetics</subject><issn>0048-9697</issn><issn>1879-1026</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1994</creationdate><recordtype>article</recordtype><recordid>eNqNkk1v1DAQhi1EVZbCPwDJB4TgELBjxx8XJFSVglSpl3K2vM5Ea5SNg-0U-AX87c5-aI8UX0b2PPPO2K8JecXZB864-siYNI1VVr-z8r1lTItGPSErbrRtOGvVU7I6Ic_I81J-MFza8HNybjhGoVbk7zVMkP1I_Tzn5MOG1kT7VIBmCGkqNS-hxjTRONG6ATqneRn9_gR-z8j11BfqkS7LWGka9lSGETxq4Db7PqJujfdAf_lSoaAU9thhdxA2WIqp_IKcDX4s8PIYL8j3L1d3l1-bm9vrb5efb5rQcVYbIYUf1rpVci1725pODFKy1jLT2XXPOmO6oMFy30mtuATbcsmVYUxpK3QbxAV5e9DF2_5coFS3jSXAOPoJ0lJci6_FNDP_AbZatDjPYyC2V0Zi-0dBoYwQkiMoD2DIqZQMg5tz3Pr8x3Hmdta7na9u56uz0u2tdwrLXh_1l_UW-lPR0WvMvznmfQl-HLKfQiwnTOKfMYoh9umAAdpwHyG7EiJMAfqIX6K6PsV_z_EAh_3JbA</recordid><startdate>19940301</startdate><enddate>19940301</enddate><creator>Degteva, Marina O.</creator><creator>Kozheurov, Vyacheslav P.</creator><creator>Vorobiova, Marina I.</creator><general>Elsevier B.V</general><general>Elsevier Science</general><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7T2</scope><scope>7TV</scope><scope>7U2</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope><scope>7TB</scope><scope>8FD</scope><scope>FR3</scope><scope>KR7</scope></search><sort><creationdate>19940301</creationdate><title>General approach to dose reconstruction in the population exposed as a result of the release of radioactive wastes into the Techa river</title><author>Degteva, Marina O. ; Kozheurov, Vyacheslav P. ; Vorobiova, Marina I.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c510t-343afb7264b4d92853f440290859bd05885c7e91a547614e921416800679372c3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1994</creationdate><topic>Adolescent</topic><topic>Adult</topic><topic>Age Factors</topic><topic>Body Burden</topic><topic>Dental Enamel - metabolism</topic><topic>Dosimetry</topic><topic>Environmental Exposure - analysis</topic><topic>External exposure</topic><topic>Fresh Water</topic><topic>Freshwater</topic><topic>Humans</topic><topic>Internal exposure</topic><topic>Radioactive contamination</topic><topic>Russia</topic><topic>Strontium</topic><topic>Strontium Radioisotopes - analysis</topic><topic>Strontium Radioisotopes - pharmacokinetics</topic><topic>Techa population</topic><topic>Tissue Distribution</topic><topic>Water Pollutants, Radioactive - analysis</topic><topic>Water Pollutants, Radioactive - pharmacokinetics</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Degteva, Marina O.</creatorcontrib><creatorcontrib>Kozheurov, Vyacheslav P.</creatorcontrib><creatorcontrib>Vorobiova, Marina I.</creatorcontrib><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Aqualine</collection><collection>Health and Safety Science Abstracts (Full archive)</collection><collection>Pollution Abstracts</collection><collection>Safety Science and Risk</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Mechanical & Transportation Engineering Abstracts</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><jtitle>The Science of the total environment</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Degteva, Marina O.</au><au>Kozheurov, Vyacheslav P.</au><au>Vorobiova, Marina I.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>General approach to dose reconstruction in the population exposed as a result of the release of radioactive wastes into the Techa river</atitle><jtitle>The Science of the total environment</jtitle><addtitle>Sci Total Environ</addtitle><date>1994-03-01</date><risdate>1994</risdate><volume>142</volume><issue>1</issue><spage>49</spage><epage>61</epage><pages>49-61</pages><issn>0048-9697</issn><eissn>1879-1026</eissn><coden>STENDL</coden><abstract>Massive releases of fission products from the plutonium production facility ‘Mayak’ resulted in the years 1949–1956 in the contamination of the river Techa and its flood lands. This led to the exposure of the population in many riverside villages due to external γ-rays and due to the incorporation of radionuclides, primarily Sr-90. The exposure situation is described and the reconstruction of doses due to external and due to internal radioactivity is explained. The internal dosimetry is based on large scale measurements of Sr-90 β-rays on the surface of teeth that were begun in 1960, and on whole-body measurements of Sr-90 that were begun in 1974. The details of the analyses are presented in Part 2 of the present report. Average doses due to the external and the internal exposure are given for the residents of the different villages along the river Techa. In the total population of about 28 000 persons that were assessed, the medium dose to the red bone marrow was about 0.25 Gy and the mean dose about 0.4 Gy. 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subjects | Adolescent Adult Age Factors Body Burden Dental Enamel - metabolism Dosimetry Environmental Exposure - analysis External exposure Fresh Water Freshwater Humans Internal exposure Radioactive contamination Russia Strontium Strontium Radioisotopes - analysis Strontium Radioisotopes - pharmacokinetics Techa population Tissue Distribution Water Pollutants, Radioactive - analysis Water Pollutants, Radioactive - pharmacokinetics |
title | General approach to dose reconstruction in the population exposed as a result of the release of radioactive wastes into the Techa river |
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