Heavy Metals In Marine Aerosols Of The Azov Sea

The content of heavy metals and Al in the aerosol matter over the Sea of Azov has been studied. According to the special test the vast majority of samples were attributed to the type of marine aerosol. The ranges of contents were determined as following: Fe (200 – 2000 ng/m3), Al (20 – 200 ng/m3), Z...

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Published in:RELIEVE - Revista Electrónica de Investigación y Evaluación Educativa
Main Authors: Marina Chichaeva A., Mikhail Lychagin Yu., Anton Syroeshkin V., Olga Chernitsova V.
Format: Article in Journal/Newspaper
Language:English
Published: Russian Geographical Society 2020
Subjects:
Online Access:https://ges.rgo.ru/jour/article/view/1166
https://doi.org/10.24057/2071-9388-2020-11
id ftjges:oai:oai.gesj.elpub.ru:article/1166
record_format openpolar
institution Open Polar
collection Geography, Environment, Sustainability (E-Journal)
op_collection_id ftjges
language English
topic heavy metals;spatial distribution;aerosol;micro particles;sea surface microlayer;pollution;Don River;Taganrog Bay
spellingShingle heavy metals;spatial distribution;aerosol;micro particles;sea surface microlayer;pollution;Don River;Taganrog Bay
Marina Chichaeva A.
Mikhail Lychagin Yu.
Anton Syroeshkin V.
Olga Chernitsova V.
Heavy Metals In Marine Aerosols Of The Azov Sea
topic_facet heavy metals;spatial distribution;aerosol;micro particles;sea surface microlayer;pollution;Don River;Taganrog Bay
description The content of heavy metals and Al in the aerosol matter over the Sea of Azov has been studied. According to the special test the vast majority of samples were attributed to the type of marine aerosol. The ranges of contents were determined as following: Fe (200 – 2000 ng/m3), Al (20 – 200 ng/m3), Zn (10 – 280 ng/m3), Cu (2 – 23 ng/m3), Ni (1 – 16 ng/m3), Pb (3 -30 ng/m3), Cd (0.4 –2.8 ng/m3); Mn (3 – 23 ng/m3), Cr (1 – 15 ng/m3). The spatial distribution of HMs in the marine aerosol of the Sea of Azov depends on the influence of the river-sea geochemical barrier zone in the Taganrog Bay and the anthropogenic impact of the coastal industrial cities. HM concentrations decrease from the northern coast of the bay and the mouth of the Don River towards the open sea. The maximum HM content in marine aerosol observed in the mouth area of the Don River. It may be associated with the HM accumulation at the river-sea geochemical barrier, and also with the anthropogenic impact of the cities of Rostov-on-Don, Azov and Taganrog. Anthropogenic impact of the city of Mariupol cause the maximum values of Fe, Cr, and Cd in marine aerosol matter of the western part of the Taganrog Bay.
format Article in Journal/Newspaper
author Marina Chichaeva A.
Mikhail Lychagin Yu.
Anton Syroeshkin V.
Olga Chernitsova V.
author_facet Marina Chichaeva A.
Mikhail Lychagin Yu.
Anton Syroeshkin V.
Olga Chernitsova V.
author_sort Marina Chichaeva A.
title Heavy Metals In Marine Aerosols Of The Azov Sea
title_short Heavy Metals In Marine Aerosols Of The Azov Sea
title_full Heavy Metals In Marine Aerosols Of The Azov Sea
title_fullStr Heavy Metals In Marine Aerosols Of The Azov Sea
title_full_unstemmed Heavy Metals In Marine Aerosols Of The Azov Sea
title_sort heavy metals in marine aerosols of the azov sea
publisher Russian Geographical Society
publishDate 2020
url https://ges.rgo.ru/jour/article/view/1166
https://doi.org/10.24057/2071-9388-2020-11
genre Antarctica Journal
Arctic
genre_facet Antarctica Journal
Arctic
op_source GEOGRAPHY, ENVIRONMENT, SUSTAINABILITY; Vol 13, No 2 (2020); 127-134
2542-1565
2071-9388
op_relation https://ges.rgo.ru/jour/article/view/1166/472
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Aryasree S, Nair PR, Girach IA, Jacob S. (2015). Winter time chemical characteristics of aerosols over the Bay of Bengal: continental influence. Environmental Science and Pollution Research, 22(19), 14901-14918, DOI:10.1007/s11356-015-4700-7.
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spelling ftjges:oai:oai.gesj.elpub.ru:article/1166 2023-05-15T14:14:54+02:00 Heavy Metals In Marine Aerosols Of The Azov Sea Marina Chichaeva A. Mikhail Lychagin Yu. Anton Syroeshkin V. Olga Chernitsova V. 2020-06-24 application/pdf https://ges.rgo.ru/jour/article/view/1166 https://doi.org/10.24057/2071-9388-2020-11 eng eng Russian Geographical Society https://ges.rgo.ru/jour/article/view/1166/472 Akinori I., Myriokefalitakis S., Kanakidou M., Mahowald N. M., et al. (2019). Pyrogenic iron: The missing link to high iron solubility in aerosols. Science Advances, 5(5), 7671, DOI:10.1126/sciadv.aau7671 . Aryasree S, Nair PR, Girach IA, Jacob S. (2015). Winter time chemical characteristics of aerosols over the Bay of Bengal: continental influence. Environmental Science and Pollution Research, 22(19), 14901-14918, DOI:10.1007/s11356-015-4700-7. Brooks S.D., Thornton D.C. (2018). Marine Aerosols and Clouds. Annual Review of Marine Science, 3(10), 289-313, DOI:10.1146/annurevmarine-121916-063148. Buseck P. R., Posfai M. (1999) Airborne minerals and related aerosol particles: Effects on climate and the environment. Proceedings of the National Academy of Sciences, 96(7), 3372–3379, DOI:10.1073/pnas.96.7.3372. Chandrakar K.K., Cantrell W., Chang K., Ciochetto D., et al. (2016). Aerosol indirect effect from turbulence-induced broadening of clouddroplet size distributions. Proceedings of the National Academy of Sciences USA, 113(50), 14243-14248, DOI:10.1175/JAS-D-18-0006.1. Coquery M., Villeneuve J.P. (2001). Final report on the split sampling exercises and quality assurance activities. EU Project № ENV RM S9602, Amsterdam, ICWC, 51. Csavina J., Field J., Taylor M.P., Gao S., et al. (2012). A Review on the Importance of Metals and Metalloids in Atmospheric Dust and Aerosol from Mining Operations. Science of the Total Environment, 433, 58-73, DOI:10.1016/j.scitotenv.2012.06.013. Fleming L.E., Bean J.A., Kirkpatrick B., Cheng Y.S., et al. (2009). Exposure and effect assessment of aerosolized red tide toxins (brevetoxins) and asthma. Environmental Health Perspectives, 117(7), 1095-100. DOI:10.1289/ehp.0900673. Furness R.W. (2017). Heavy Metals in the Marine Environment. CRC press. Garrett W.D. (1965). Collection of slick-forming materials from the sea surface. // Limnol. Oceanog, 10, 602-605. . Georgoulias A.K., Alexandri G., Kourtidis K.A., Lelieveld J., et al. (2016). Spatiotemporal variability and contribution of different aerosol types to the Aerosol Optical Depth over the Eastern Mediterranean. Atmospheric Chemistry And Physics, 16(21), 13853-13884, DOI:10.5194/acp-1613853-2016. Golubeva N.I., Burtseva L.V., Gromov S.A. (2011). Heavy Metals in Atmospheric Air in the Kara Sea Water Area in September–October. Oceanology, 58, 870-878. DOI: doi.org/10.1134/S000143701806005X. Goncharuk V.V., Lapshin V.B., Chichaeva M.A., Samsoni-Todorov A.O., et al. (2012). Heavy metals, aluminum and arsenic in aerosols of the oceans. Chemistry and Water Technology, 34(1), 1-15, DOI:10.3103/S1063455X12010018. Gordeev V.V. (1983). River runoff into the ocean and features of its geochemistry. Moscow: Nauka. Grebennikova T.V., Syroeshkin A.V., Chichaeva M.A., Esper S.A., Lvov D.K. (2017). Natural foci of influenza A in the western Arctic. Voprosy Virusologii, 62(1), 11-17, DOI:10.18821/0507-4088-2017-62-1-11-17. Grishchenko S.V., Grishchenko I.S., Kostenko V.S., Basenko I.N. et al. (2018). Hygienic assessment of atmospheric air pollution of populated areas of Donbass by heavy metals. Bulletin of Hygiene and Epidemiology, 22(1), 11-15. Izhar S., Goel A., Chakraborty A., Gupta T. Annual trends in occurrence of submicron particles in ambient air and health risk posed by particle bound metals. (2016). Chemosphere, 146, 582-590, DOI:10.1016/j.chemosphere.2015.12.039. Jordi A., Basterretxea G., Tovar-Sánchez A., Alastuey A., Querol X. (2012). Copper aerosols inhibit phytoplankton growth in the Mediterranean Sea. Proceedings of the National Academy of Sciences USA, 109(52), 21246-21249, DOI:10.1073/pnas.1207567110. Kirkpatrick B., Fleming L.E., Bean J.A., Nierenberg K., et al. (2011). Aerosolized Red Tide Toxins (Brevetoxins) and Asthma: Continued health effects after 1 hour beach exposure. Harmful Algae, 10(2), 138-143, DOI:10.1016/j.hal.2010.08.005. Kolesnikov M.V., Matveeva I.S., Lapshin V.B., Pletenev S.S., et al. (2005). Heavy metals in marine aerosols of the Russian part of the Black sea. Oceanology, 45(1), 102-111. Lang-Yona N., Lehahn Y., Herut B., Burshtein N., Rudich Y. (2014) Marine aerosol as a possible source for endotoxins in coastal areas. Science of the Total Environment, 499, 311-8, DOI:10.1016/j.scitotenv.2014.08.054. Li J., Han Z., Yao X., Xie Z., Tan S. (2019). The distributions and direct radiative effects of marine aerosols over East Asia in springtime. Sci Total Environ. 651(2), 1913–1925, DOI:10.1016/j.scitotenv.2018.09.368. Li S., Du L., Tsona N.T., Wang W. (2018). The interaction of trace heavy metal with lipid monolayer in the sea surface microlayer. Chemosphere. 196, 323-330. DOI:10.1016/j.chemosphere.2017.12.157. Liu Y., Li S., Sun C., Qi M., et al. (2018) Pollution Level and Health Risk Assessment of PM2.5-Bound Metals in Baoding City Before and After the Heating Period. International Journal of Environmental Research and Public Health, 15(10), 2286. DOI:10.3390/ijerph15102286. Mahowald N.M., Hamilton D.S., Mackey K.R., Moore J.K., et al. (2018). Aerosol trace metal leaching and impacts on marine microorganisms. Nature Communications, 9(1), 2614, DOI:10.1038/s41467-018-04970-7. Marín-Beltrán I., Logue J.B., Andersson A.F., Peters F. (2019). Atmospheric Deposition Impact on Bacterial Community Composition in the NW Mediterranean. Frontiers in Microbiology, 10(858), 1-14, DOI:10.3389/fmicb.2019.00858. 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Авторы, публикующие в данном журнале, соглашаются со следующим:Авторы сохраняют за собой авторские права на работу и предоставляют журналу право первой публикации работы на условиях лицензии Creative Commons Attribution License, которая позволяет другим распространять данную работу с обязательным сохранением ссылок на авторов оригинальной работы и оригинальную публикацию в этом журнале.Авторы сохраняют право заключать отдельные контрактные договорённости, касающиеся не-эксклюзивного распространения версии работы в опубликованном здесь виде (например, размещение ее в институтском хранилище, публикацию в книге), со ссылкой на ее оригинальную публикацию в этом журнале.Авторы имеют право размещать их работу CC-BY GEOGRAPHY, ENVIRONMENT, SUSTAINABILITY; Vol 13, No 2 (2020); 127-134 2542-1565 2071-9388 heavy metals;spatial distribution;aerosol;micro particles;sea surface microlayer;pollution;Don River;Taganrog Bay info:eu-repo/semantics/article info:eu-repo/semantics/publishedVersion 2020 ftjges https://doi.org/10.24057/2071-9388-2020-11 https://doi.org/10.1126/sciadv.aau7671 https://doi.org/10.1007/s11356-015-4700-7 https://doi.org/10.1146/annurevmarine-121916-063148 https://doi.org/10.1073/pnas.96.7.3372 https://doi.org/10.1175/JAS-D- 2021-05-21T07:34:36Z The content of heavy metals and Al in the aerosol matter over the Sea of Azov has been studied. According to the special test the vast majority of samples were attributed to the type of marine aerosol. The ranges of contents were determined as following: Fe (200 – 2000 ng/m3), Al (20 – 200 ng/m3), Zn (10 – 280 ng/m3), Cu (2 – 23 ng/m3), Ni (1 – 16 ng/m3), Pb (3 -30 ng/m3), Cd (0.4 –2.8 ng/m3); Mn (3 – 23 ng/m3), Cr (1 – 15 ng/m3). The spatial distribution of HMs in the marine aerosol of the Sea of Azov depends on the influence of the river-sea geochemical barrier zone in the Taganrog Bay and the anthropogenic impact of the coastal industrial cities. HM concentrations decrease from the northern coast of the bay and the mouth of the Don River towards the open sea. The maximum HM content in marine aerosol observed in the mouth area of the Don River. It may be associated with the HM accumulation at the river-sea geochemical barrier, and also with the anthropogenic impact of the cities of Rostov-on-Don, Azov and Taganrog. Anthropogenic impact of the city of Mariupol cause the maximum values of Fe, Cr, and Cd in marine aerosol matter of the western part of the Taganrog Bay. Article in Journal/Newspaper Antarctica Journal Arctic Geography, Environment, Sustainability (E-Journal) RELIEVE - Revista Electrónica de Investigación y Evaluación Educativa 21 2