Oil Pier at Cape Manganari (Sevastopol) as a Source of Anthropogenic Suspension and Dissolved Oil Products Based on Numerical Modeling and Expedition Data

P. D. Lomakin, Yu. N. Ryabtsev, A. I. Chepyzhenko

Marine Hydrophysical Institute of RAS, Sevastopol, Russian Federation

e-mail: p_lomakin@mail.ru

Abstract

Purpose. The purpose of the study is to identify the patterns of propagation of anthropogenic suspended matter and dissolved oil products conditioned by operation of the oil pier located at Cape Manganari in the Sevastopol region, to assess the linear scale of its impact on the surrounding water environment, as well as to determine the parts of water area which are subjected to maximum anthropogenic load.

Methods and Results. Application of the numerical modeling methods, namely the Felzenbaum three-dimensional barotropic linear model generalized for the case of Rayleigh friction, made it possible to reveal the patterns of anthropogenic suspended matter distribution by wind currents from the area where the oil pier was located. It is established that depending on the wind direction, the suspended matter flow spreads from the head of oil pier to the open sea and penetrates into the neighboring bays. The data obtained during the expeditions in the adjacent Kazachya, Kamyshovaya and Abramov bays permitted to examine the structure of the concentration fields of suspended matter and dissolved oil products as an indirect indicator of distribution of these substances. The most polluted areas of the region under study were revealed. The radius of the oil pier impact upon the surrounding water area is assessed.

Conclusions. The modeling results are confirmed by the expedition research data. According to the performed model calculations and the analysis of observational data, the radius of pier impact upon the surrounding water environment is estimated to be 0.5–1.0 miles, and the maximum anthropogenic load falls on the northern halves of the Kazachya and Kamyshovaya bays. At the north-eastern and northern winds, the anthropogenic suspended matter and oil products are accumulated in the northern part of Kazachya Bay, at the western and north-western winds, these pollutants penetrate into Kamyshovaya Bay, and when the wind is southwestern – into Abramov Bay.

Keywords

modeling, wind, total suspended matter, oil pier, Sevastopol bays, Black Sea

Acknowledgements

The study was carried out within the framework of state assignment of FSBSI FRC MHI FNNN-2024-0016.

About the authors

Pavel D. Lomakin, Leading Researcher, Marine Hydrophysical Institute of RAS (2 Kapitanskaya Str., Sevastopol, 299011, Russian Federation), DSc. (Geogr.), Professor, ResearcherID: V-7761-2017, Scopus Author ID: 6701439810, SPIN-code: 5419-9884, p_lomakin@mail.ru

Yuri N. Ryabtsev, Researcher, Marine Hydrophysical Institute of RAS (2 Kapitanskaya Str., Sevastopol, 299011, Russian Federation), ORCID ID: 0000-0002-9682-9969, ResearcherID: ABE-4315-2022, Scopus Author ID: 6506665265, SPIN-code: 7853-4597, ruab@mail.ru

Alexey I. Chepyzhenko, Senior Researcher, Marine Hydrophysical Institute of RAS (2 Kapitanskaya Str., Sevastopol, 299011, Russian Federation), CSc. (Tech.), ORCID ID: 0000-0002-6763-7140, WOSResearcherID: AAG-7929-2020, Scopus Author ID: 6504344211, SPIN-code: 3599-9653, ecodevice@yandex.ru

Original russian text

Original Russian Text © P. D. Lomakin, Yu. N. Ryabtsev, A. I. Chepyzhenko, 2026, published in MORSKOY GIDROFIZICHESKIY ZHURNAL, Vol. 42, Iss. 3, pp. 422–435 (2026)

For citation

Lomakin, P.D., Ryabtsev, Yu.N. and Chepyzhenko, A.I., 2026. Oil Pier at Cape Manganari (Sevastopol) as a Source of Anthropogenic Suspension and Dissolved Oil Products Based on Numerical Modeling and Expedition Data. Physical Oceanography, 33(3), pp. 458-470.

References

  1. Ivanov, V.A., Ovsyany, E.I., Repetin, L.N., Romanov, A.S. and Ignatyeva, O.G., 2006. Hydrological and Hydrochemical Regime of the Sebastopol Bay and Its Changing under Influence of Climatic and Anthropogenic Factors. Sevastopol: MHI NAS of Ukraine, 90 p. (in Russian).
  2. Alyomov, S.V., 2009. Ecological Quality Assessment of Port Aquatoria in Sevastopol Region by Use of Macrobenthic Community Characteristics. Ecological Safety of Coastal and Shelf Zones and Comprehensive Use of Shelf Resources, 18, pp. 19-29 (in Russian).
  3. Dulov, B.A., Yurovskaya, M.V. and Kozlov, I.E., 2015. Coastal Zone of Sevastopol on High Resolution Satellite Images. Physical Oceanography, (6), pp. 39-54. https://doi.org/10.22449/1573-160X-2015-6-39-54
  4. Belokopytov, V.N., Kubryakov, A.I. and Pryakhina, S.F., 2019. Modelling of Water Pollution Propagation in the Sevastopol Bay. Physical Oceanography, 26(1), pp. 3-12. https://doi.org/10.22449/1573-160X-2019-1-3-12
  5. Gruzinov, V.M., Dyakov, N.N., Mezenceva, I.V., Malchenko, Yu.A., Zhohova, N.V. and Korshenko, A.N., 2019. Sources of Coastal Water Pollution near Sevastopol. Oceanology, 59(4), pp. 523-532. https://doi.org/10.1134/S0001437019040076
  6. Lomakin, P.D. and Chepyzhenko, A.A., 2019. Hydrophysical Conditions and Characteristics of Water Pollution of the Kazachya Bay (Crimea Region) in September of the Year 2018. Monitoring Systems of Environment, (1), pp. 48-54. https://doi.org/10.33075/2220-5861-2019-1-48-54 (in Russian).
  7. Lomakin, P.D., Chepyzhenko, A.I. and Grebneva, E.A., 2020. Structure of Fields of Oceanological Quantities in the Kamyshovaya Bay (Crimea) in November 2019. Monitoring Systems of Environment, (2), pp. 29-35. https://doi.org/10.33075/2220-5861-2020-2-29-35 (in Russian).
  8. Lomakin, P.D., Chepyzhenko, A.I. and Grebneva, E.A., 2020. Fields of Oceanological Characteristics in the Abramova Bay (Sevastopol) in November 2019. Ecological Safety of Coastal and Shelf Zones of Sea, (2), pp. 68-79. https://doi.org/10.22449/2413-5577-2020-2-68-79 (in Russian).
  9. Zhang, C. and Yang, J.-Q., 2024. Prevention and Control of Ship-Source Pollution in the Arctic Shipping Routes: Challenges and Countermeasures. Environmental Science and Pollution Research, 31, pp. 40436-40444. https://doi.org/10.1007/s11356-023-30817-w
  10. Fan, L., Yang, H. and Zhang, X., 2024. Targeting the Effectiveness Assessment of the Emission Control Policies on the Shipping Industry. Sustainability, 16(6), 2465. https://doi.org/10.3390/su16062465
  11. Aziz, H.A., Ariffin, K.S., Wang, M.-H.S. and Wang, L.K., 2024. Dredging and Mining Operations, Management, and Environmental Impacts. In: L. K. Wang, M. H. S. Wang and Y. T. Hung, eds., 2024. Industrial Waste Engineering. Handbook of Environmental Engineering. HEE Series, vol. 28. Cham: Springer International Publishing, pp. 333-396. https://doi.org/10.1007/978-3-031-46747-9_8
  12. Eisma, D., 1993. Suspended Matter in the Aquatic Environment. Berlin, Heidelberg: Springer, 315 p. https://doi.org/10.1007/978-3-642-77722-6
  13. Behrens, S., Griffin, D., Hayward, J., Hemer, M., Knight, C., McGarry, S., Osman, P. and Wright, J., 2012. Ocean Renewable Energy: 2015–2050: An Analysis of Ocean Energy in Australia. North Ryde: CSIRO, 212 p. https://doi.org/10.4225/08/584af1865b172
  14. Shapiro, N.B., 2006. Modeling of the Currents on the Seaside Nearby Sevastopol City. Ecological Safety of Coastal and Shelf Zones and Comprehensive Use of Shelf Resources, 14, pp. 119-134 (in Russian).
  15. Mikhailova, E.N., Shapiro, N.B. and Yushchenko, S.A., 2001. Modelling of the Propagation of Passive Impurities in Sevastopol Bays. Physical Oceanography, 11(3), pp. 233-247. https://doi.org/10.1007/BF02508870
  16. Burchard, H. and Rennau, H., 2008. Comparative Quantification of Physically and Numerically Induced Mixing in Ocean Models. Ocean Modelling, 20(3), pp. 293-311. https://doi.org/10.1016/j.ocemod.2007.10.003
  17. Hofmeister, R., Beckers, J.-M. and Burchard, H., 2011. Realistic Modeling of the Exceptional Inflows into the Central Baltic Sea in 2003 Using Terrain-Following Coordinates. Ocean Modelling, 39(3–4), pp. 233-247. https://doi.org/10.1016/j.ocemod.2011.04.007
  18. Fofonova, V., Kärnä, T., Klingbeil, K., Androsov, A., Kuznetsov, I., Sidorenko, D., Danilov, S., Burchard, H. and Wiltshire, K.H., 2021. Plume Spreading Test Case for Coastal Ocean Models. Geoscientific Model Development, 14(11), pp. 6945-6975. https://doi.org/10.5194/gmd-14-6945-2021
  19. Ocean Studies Board, 2003. Oil in the Sea III: Inputs, Fates, and Effects. Washington, D.C.: National Academies Press, 277 p. https://doi.org/10.17226/10388
  20. Chapman, P.M., Hayward, A. and Faithful, J., 2017. Total Suspended Solids Effects on Freshwater Lake Biota Other than Fish. Bulletin of Environmental Contamination and Toxicology, 99(4), pp. 423-427. https://doi.org/10.1007/s00128-017-2154-y
  21. Lomakin, P.D. and Chepyzhenko, A.I., 2025. Natural and Anthropogenic Total Suspended Matter in the Coastal Waters of the Heraclean Peninsula (Black Sea). _Environmental Control System_s, (1), pp. 61-70. https://doi.org/10.33075/2220-5861-2025-1-61-70 (in Russian).
  22. Holdway, D., Radlinski, A., Exon, N., Auzende, J.-M. and Van de Beuque, S., 2000. Continuous Multi-Spectral Fluorescence and Absorption for Petroleum Hydrocarbon Detection in Near-Surface Ocean Waters: ZoNeC05 Survey, Fairway Basin Area, Lord Howe Rise. Canberra: Australian Geological Survey Organization. Record 2000/35, 57 p. Available at: https://d28rz98at9flks.cloudfront.net/34232/Rec2000_035.pdf [Accessed: 3 February 2026].
  23. Lomakin, P.D. and Chepyzhenko, A.I., 2020. Field of the Dissolved Oil Products Concentration in the Sevastopol Bay Waters (the Black Sea). Physical Oceanography, 27(2), pp. 142-151. https://doi.org/10.22449/1573-160X-2020-2-142-151

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