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<article article-type="research-article" dtd-version="1.3" xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xml:lang="ru"><front><journal-meta><journal-id journal-id-type="publisher-id">radhyd</journal-id><journal-title-group><journal-title xml:lang="ru">Радиационная гигиена</journal-title><trans-title-group xml:lang="en"><trans-title>Radiatsionnaya Gygiena = Radiation Hygiene</trans-title></trans-title-group></journal-title-group><issn pub-type="ppub">1998-426X</issn><issn pub-type="epub">2409-9082</issn><publisher><publisher-name>NIIRG</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.21514/1998-426X-2019-12-4-37-46</article-id><article-id custom-type="elpub" pub-id-type="custom">radhyd-656</article-id><article-categories><subj-group subj-group-type="heading"><subject>Research Article</subject></subj-group><subj-group subj-group-type="section-heading" xml:lang="ru"><subject>Научные статьи</subject></subj-group><subj-group subj-group-type="section-heading" xml:lang="en"><subject>Scientific articles</subject></subj-group></article-categories><title-group><article-title>Корреляция между расчетными и измеренными значениями мощности дозы гамма-излучения в воздухе в лесах, загрязненных 137Cs: отдаленный период после Чернобыльской аварии</article-title><trans-title-group xml:lang="en"><trans-title>Correlation between calculated and measured values of gamma dose rate in air in forests contaminated with 137Cs: the remote period after the Chernobyl accident</trans-title></trans-title-group></title-group><contrib-group><contrib contrib-type="author" corresp="yes"><name-alternatives><name name-style="eastern" xml:lang="ru"><surname>Рамзаев</surname><given-names>В. П.</given-names></name><name name-style="western" xml:lang="en"><surname>Ramzaev</surname><given-names>Valery P.</given-names></name></name-alternatives><bio xml:lang="ru"><p>Рамзаев Валерий Павлович – кандидат медицинских наук, ведущий научный сотрудник лаборатории внешнего облучения</p><p>197101, Санкт-Петербург, ул. Мира, д. 8</p></bio><bio xml:lang="en"><p>Candidate of Medical Sciences, Leading Researcher of the Laboratory of External Exposure</p><p>Mira Str., 8, Saint-Petersburg, 197101</p></bio><email xlink:type="simple">V.Ramzaev@mail.ru</email><xref ref-type="aff" rid="aff-1"/></contrib><contrib contrib-type="author" corresp="yes"><name-alternatives><name name-style="eastern" xml:lang="ru"><surname>Барковский</surname><given-names>А. Н.</given-names></name><name name-style="western" xml:lang="en"><surname>Barkovsky</surname><given-names>Anatoly N.</given-names></name></name-alternatives><bio xml:lang="ru"><p>Барковский Анатолий Николаевич – руководитель Федерального радиологического центра, главный научный сотрудник</p><p>197101, Санкт-Петербург, ул. Мира, д. 8</p></bio><bio xml:lang="en"><p>Head of the Federal Radiological Centre</p><p>Mira Str., 8, Saint-Petersburg, 197101</p></bio><xref ref-type="aff" rid="aff-1"/></contrib></contrib-group><aff-alternatives id="aff-1"><aff xml:lang="ru"><institution>Санкт-Петербургский научно-исследовательский институт радиационной гигиены имени профессора П.В. Рамзаева, Федеральная служба по надзору в сфере защиты прав потребителей и благополучия человека</institution><country>Россия</country></aff><aff xml:lang="en"><institution>Saint-Petersburg Research Institute of Radiation Hygiene after Professor P.V. Ramzaev, Federal Service for Surveillance on Consumer Rights Protection and Human Well-Being</institution><country>Russian Federation</country></aff></aff-alternatives><pub-date pub-type="collection"><year>2019</year></pub-date><pub-date pub-type="epub"><day>06</day><month>01</month><year>2020</year></pub-date><volume>12</volume><issue>4</issue><fpage>37</fpage><lpage>46</lpage><permissions><copyright-statement>Copyright &amp;#x00A9; Рамзаев В.П., Барковский А.Н., 2020</copyright-statement><copyright-year>2020</copyright-year><copyright-holder xml:lang="ru">Рамзаев В.П., Барковский А.Н.</copyright-holder><copyright-holder xml:lang="en">Ramzaev V.P., Barkovsky A.N.</copyright-holder><license xml:lang="ru" license-type="creative-commons-attribution" xlink:href="https://creativecommons.org/licenses/by/4.0/" xlink:type="simple"><license-p>Данная работа распространяется под лицензией Creative Commons Attribution 4.0.</license-p></license><license xml:lang="en" license-type="creative-commons-attribution" xlink:href="https://creativecommons.org/licenses/by/4.0/" xlink:type="simple"><license-p>This work is licensed under a Creative Commons Attribution 4.0 License.</license-p></license></permissions><self-uri xlink:href="https://www.radhyg.ru/jour/article/view/656">https://www.radhyg.ru/jour/article/view/656</self-uri><abstract><p>В 2015–2016 гг. было обследовано 13 лесных и 7 целинных луговых участков, расположенных на территории юго-западных районов Брянской области. Целью работы являлась экспериментальная проверка возможности использования метода расчета мощности дозы гамма-излучения в воздухе в радиоактивно загрязненных лесах на отдаленном этапе после Чернобыльской аварии. По результатам гамма-спектрометрического анализа проб почвы, отобранных на участках, были установлены и опубликованы значения запаса и вертикального распределения 137Cs в верхнем 20-сантиметровом слое. Эти данные были использованы для вычисления мощности воздушной кермы с применением метода, заимствованного из литературы. Кроме того, в местах отбора проб почвы была измерена мощность амбиентного эквивалента дозы гамма-излучения в воздухе, и с помощью полевого гамма-спектрометра-дозиметра был определен вклад 137Cs в общую мощность дозы. Измеренные значения мощности амбиентного эквивалента дозы от 137Cs положительно и статистически значимо коррелировали с расчетными значениями мощности воздушной кермы. Коэффициент корреляции Спирмена был равен 0,989 (P &lt; 0,01) для локации «Лес» и 0,893 (P &lt; 0,05) для локации «Луг». Статистически значимых различий между локациями «Лес» и «Луг» при анализе соотношения измеренных и расчетных значений мощности дозы выявлено не было (тест Манна – Уитни, Р &gt; 0,05). Результаты настоящей работы показывают, что при вычислении мощности дозы гамма-излучения в воздухе в лесу на отдаленном этапе после Чернобыльской аварии достаточно знать величину запаса 137Cs в верхнем 20-сантиметровом слое почвы и подробную картину вертикального распределения радионуклида в этом слое. Присутствием древесной биомассы можно пренебречь. Такая оценка мощности дозы является консервативной. Однако степень завышения мощности дозы в воздухе будет невелика – в пределах +10%, что вполне приемлемо для определения дозы внешнего облучения человека при его нахождении в радиоактивно загрязненном лесу.</p></abstract><trans-abstract xml:lang="en"><p>In 2015–2016, 13 forest and 7 virgin grassland plots located in the south-western districts of the Bryansk region were surveyed. The aim of the work was to experimentally test the possibility of using a method for calculating the dose rate of gamma radiation in air in radioactively contaminated forests in a remote period after the Chernobyl accident. According to the results of gamma-spectrometric analysis of soil samples obtained at the sites in another study, the values of inventory and vertical distribution of 137Cs in the upper 20 cm layer were established. In this paper, these data were used to calculate the air kerma rate using a method taken from literature. In addition, at the sites of soil sampling, ambient dose equivalent rate in air was measured, and the contribution of 137Cs to the total gamma dose rate was determined with a field gamma spectrometer-dosemeter. The measured values of the ambient dose equivalent rate from 137Cs correlated positively and statistically significantly with the calculated values of the air kerma rate. The Spearman correlation coefficient was 0.989 (P &lt; 0.01) for the location “forest” and 0.893 (P &lt; 0.05) for the location “grassland”. There was no statistically significant difference between the “forest” and “grassland” locations when analyzing the ratio of the measured dose rate values to the calculated dose rate values (the Mann-Whitney U test, P &gt; 0.05). Results of this work show that, when calculating gamma radiation dose rate in air in forests at a remote stage after the Chernobyl accident, it is enough to know the 137Cs inventory in the upper 20 cm soil layer and a detailed picture of vertical distribution of the radionuclide in this layer. The presence of woody biomass can be neglected. This dose rate estimate is conservative. However, a degree of overestimation of the dose rate in air is small, within +10%, which is quite acceptable for determining the external effective dose rate for an individual in the radioactively contaminated forest.</p></trans-abstract><kwd-group xml:lang="ru"><kwd>лес</kwd><kwd>луг</kwd><kwd>почва</kwd><kwd>137Cs</kwd><kwd>воздушная керма</kwd><kwd>амбиентный эквивалент дозы</kwd></kwd-group><kwd-group xml:lang="en"><kwd>forest</kwd><kwd>grassland</kwd><kwd>soil</kwd><kwd>137Cs</kwd><kwd>air kerma</kwd><kwd>ambient dose equivalent</kwd></kwd-group></article-meta></front><back><ref-list><title>References</title><ref id="cit1"><label>1</label><citation-alternatives><mixed-citation xml:lang="ru">Shaw, G. Radionuclides in forest ecosystems. Radioactivity Environ., 2007, Vol. 10, pp. 127–155.</mixed-citation><mixed-citation xml:lang="en">Shaw, G. Radionuclides in forest ecosystems. 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