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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">tinro</journal-id><journal-title-group><journal-title xml:lang="ru">Известия ТИНРО</journal-title><trans-title-group xml:lang="en"><trans-title>Izvestiya TINRO</trans-title></trans-title-group></journal-title-group><issn pub-type="ppub">1606-9919</issn><issn pub-type="epub">2658-5510</issn><publisher><publisher-name>ТИНРО</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.26428/1606-9919-2017-189-147-155</article-id><article-id custom-type="elpub" pub-id-type="custom">tinro-190</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>УСЛОВИЯ ОБИТАНИЯ ПРОМЫСЛОВЫХ ОБЪЕКТОВ</subject></subj-group><subj-group subj-group-type="section-heading" xml:lang="en"><subject>ENVIRONMENTS OF FISHERIES RESOURCES</subject></subj-group></article-categories><title-group><article-title>Микроэлементы (As, Cd, Pb, Fe, Cu, Zn, Se, Hg) в промысловых ракообразных Японского моря</article-title><trans-title-group xml:lang="en"><trans-title>Microelements (As, Cd, Pb, Fe, Cu, Zn, Se, Hg) in commercial crustaceans in the Japan Sea</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>Наревич</surname><given-names>Ирина Сергеевна</given-names></name><name name-style="western" xml:lang="en"><surname>Narevich</surname><given-names>Irina S.</given-names></name></name-alternatives><email xlink:type="simple">Irishka.k.89@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>Ковековдова</surname><given-names>Лидия Тихоновна</given-names></name><name name-style="western" xml:lang="en"><surname>Kovekovdova</surname><given-names>Lidia T.</given-names></name></name-alternatives><email xlink:type="simple">Kovekovdova@mail.ru</email><xref ref-type="aff" rid="aff-1"/></contrib></contrib-group><aff xml:lang="ru" id="aff-1"><institution>Тихоокеанский научно-исследовательский рыбохозяйственный центр</institution><country>Russian Federation</country></aff><pub-date pub-type="collection"><year>2017</year></pub-date><pub-date pub-type="epub"><day>30</day><month>06</month><year>2017</year></pub-date><volume>189</volume><issue>2</issue><fpage>147</fpage><lpage>155</lpage><permissions><copyright-statement>Copyright &amp;#x00A9; Наревич И.С., Ковековдова Л.Т., 2017</copyright-statement><copyright-year>2017</copyright-year><copyright-holder xml:lang="ru">Наревич И.С., Ковековдова Л.Т.</copyright-holder><copyright-holder xml:lang="en">Narevich I.S., Kovekovdova L.T.</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://izvestiya.tinro-center.ru/jour/article/view/190">https://izvestiya.tinro-center.ru/jour/article/view/190</self-uri><abstract><p>Определены уровни концентраций элементов в промысловых ракообразных Chionoecetes opilio, Paralithodes camtschaticus, Pandalus borealis, P. hypsinotus, Sclerocrangon salebrosa из Японского моря. Расположение элементов в мягких тканях ракообразных в порядке убывания концентраций имеет следующий вид: Zn &gt; Fe &gt; As &gt; Cu &gt; Se &gt; Cd ~ ~ Pb ~ Hg. Выделены особенности микроэлементного состава исследованных организмов. Отмечен повышенный уровень содержания меди в тканях ракообразных, что обусловлено ролью меди в процессах тканевого дыхания и формировании экзоскелета. Показано сходство микроэлементного состава мышечных тканей креветок и крабов. Выявлено превышение предельно допустимых уровней As в 17,5 % проанализированных особей P. borealis , в 33,3 % - P. hypsinotus , в 17,0 % - C. opilio , в 68,0 % - P. camtschaticus , в 35,5 % - S. salebrosa. </p></abstract><trans-abstract xml:lang="en"><p>Concentrations of As, Cd, Pb, Hg, Se, Fe, Cu, and Zn in tissues of the commercial crabs and shrimps Chionoecetes opilio, Paralithodes camtschaticus, Pandalus borealis, Pandalus hypsinotus , and Sclerocrangon salebrosa from Primorye waters are determined. The samples were collected by research vessels of Pacific Fish. Res. Center (TINRO) in 2012-2016. Content of metals and arsenic in the soft tissues (from claws and phalanxes of crabs and abdomen of shrimps) was determined by atomic absorption analysis (fiery and flameless methods), using Shimadzu AA-6800 spectrophotometer and mercury analyzer DMA-80 Milestone. As, Cd and Pb concentrations were measured by electrothermal method, with graphite cuvette as an atomizer; Fe, Cu and Zn concentrations were measured in the acetylene/air flame, with single-slot burner as an atomizer and background correction by a deuterium lamp. The standard solutions of the metals were used for calibration. Generally, the microelement composition in soft tissues of all shrimp and crab species is similar. For all species, concentrations of the elements in the soft tissues decrease in the order: Zn &gt; Fe &gt; As &gt; Cu &gt; Se &gt; Cd ~ Pb ~ Hg. All samples are distinguished by heightened concentration of Cu. The following ranges of the toxic metals concentration are observed (mg per kg of wet weight): Pandalus borealis As - 1.6-8.5; Cd - 0.03-0.15; Pb - 0.01-0.02; Pandalus hipsinotus As - 2.78-14.6; Cd - 0.01-0.13; Pb - 0.00-0.01; Sclerocrangon salebrosa As - 5.4-17.3; Cd - 0.01-0.04; Pb - 0.01-0.03; Chionoecetes opilio As - 9.4-14.0; Cd - 0.01-0.05; Pb - 0.01-0.05; Paralithodes camtschaticus As - 3.0-8.8; Cd - 0.0008-0.10; Pb - 0.001-0.009. Cases of exceeding the maximum permissible level of As are detected for all species: in 68.0 % of samples for Paralithodes camtschaticus , in 35.0 % of samples for Sclerocrangon salebrosa , in 33.3 % of samples for Panadalus hipsinotus , in 17.5 % of samples for Panadalis borealis , and in 17.0 % of samples for Chionoecetes opilio .</p></trans-abstract><kwd-group xml:lang="ru"><kwd>промысловые ракообразные</kwd><kwd>металлы</kwd><kwd>мышьяк</kwd><kwd>атомная абсорбция</kwd><kwd>предельно допустимый уровень</kwd></kwd-group><kwd-group xml:lang="en"><kwd>crab</kwd><kwd>shrimp</kwd><kwd>toxic metal</kwd><kwd>arsenic</kwd><kwd>atomic absorption</kwd><kwd>maximum permissible level</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">Виноградов А.П. 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