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Your search keyword '"Mazurkiewicz, Mikołaj"' showing total 19 results
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19 results on '"Mazurkiewicz, Mikołaj"'

4. Skeletal mineralogy of marine calcifying organisms shaped by seawater temperature and evolutionary history—A case study of cheilostome bryozoans

Author

Piwoni‐Piórewicz, Anna, primary, Liow, Lee Hsiang, additional, Krzemińska, Małgorzata, additional, Chełchowski, Maciej, additional, Iglikowska, Anna, additional, Ronco, Fabrizia, additional, Mazurkiewicz, Mikołaj, additional, Smith, Abigail M., additional, Gordon, Dennis P., additional, Waeschenbach, Andrea, additional, Najorka, Jens, additional, Figuerola, Blanca, additional, Boonzaaier‐Davids, Melissa K., additional, Achilleos, Katerina, additional, Mello, Hannah, additional, Florence, Wayne K., additional, Vieira, Leandro M., additional, Ostrovsky, Andrew N., additional, Shunatova, Natalia, additional, Porter, Joanne S., additional, Sokolover, Noga, additional, Cumming, Robyn L., additional, Novosel, Maja, additional, O'Dea, Aaron, additional, Lombardi, Chiara, additional, Jain, Sudhanshi S., additional, Huang, Danwei, additional, and Kukliński, Piotr, additional

Published
2024
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12. First records of Lacydonia eliasoni Hartmann-Schröder, 1996 (Polychaeta: Phyllodocida) in the European Arctic

Author

Mazurkiewicz Mikołaj, Gromisz Sławomira, Legeżyńska Joanna, and Włodarska-Kowalczuk Maria

Subjects
Arctic, Spitsbergen, Polychaeta, Lacydonia, range extension, Geology, QE1-996.5
Abstract

Lacydonia (Polychaeta: Phyllodocida) is a poorly known genus containing 16 species that are sporadically collected in low densities all over the world oceans. During three cruises (in June 2014 in Ullsfjorden, northern Norway, in January 2015 in Kongsfjorden, and in June 2012 in Smeerenburg, Svalbard) nine specimens of Lacydonia eliasoni were found on sandy and muddy sediments at depths from 180 to 350 m. All specimens were incomplete and consisted of 10 to 29 chaetigers. This study presents the first record of the Lacydonia genus in the waters of Svalbard as well as the first record of L. eliasoni in coastal waters off northern Norway. This species has been reported previously in the Skagerrak and Trondheimsfjorden (southern Norway), our findings therefore may indicate a northward extension of its range, possibly due to climate changes.

Published
2017
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13. Report on marine plastic contaminant monitoring

Author

Mazurkiewicz, Mikołaj and Palacz, Artur

Subjects
seafloor litter, beach litter, microplastic
Abstract

This milestone report describes the current capacity to monitor or otherwise observe selected indicators of marine litter pollution which have the potential to be reported consistently on a regional to global scale in support of the stakeholder needs., {"references":["Programmi di Monitoraggio per la Strategia Marina Art. 11, D.lgs. 190/2010","B. Wenneker, L. Oosterbaan, & Intersessional Correspondence Group on Marine Litter (ICGML), Guideline for Monitoring Marine Litter on the Beaches in the OSPAR Maritime Area. Edition 1.0 (London, UK, 2010). https://doi.org/10.25607/OBP-968","MSFD GES Technical Subgroup on Marine Litter (TSG-ML), Monitoring Guidance for Marine Litter in European Seas Draft Report. (2013)","Cheshire, A.C., E. Adler, J. Barbière, Y. Cohen, S. Evans, S. Jarayabhand, L. Jeftic, R. T. Jung, S. Kinsey, E. T. Kusui, I. Lavine, P. Manyara, L. Oosterbaan, M. A. Pereira, S. Sheavly, A. Tkalin, S. Varadarajan, B. Wenneker, & G. Westphalen, UNEP/IOC Guidelines on Survey and Monitoring of Marine Litter (2009)","MARLIN Baltic Marine Litter Project, Final Report of Baltic Marine Litter Project Marlin - Litter Monitoring and Raising Awareness 2011-2013 (2013)","T. Maes & F. Preston-Whyte, The African Marine Litter Outlook (2023)","S. Lippiatt, S. Opfer, & C. Arthur, Marine debris monitoring and assessment. NOAA Technical Memorandum, (2013)","H. K. Burgess, C. E. Herring, S. Lippiatt, S. Lowe, & A. V Uhrin, NOAA Marine Debris Monitoring and Assessment Project Shoreline Survey Guide. NOAA Technical Memorandum NOS OR&R 56, 20 (2021) 1–20. https://doi.org/10.25923/g720-2n18","EMODnet Chemistry, European floating micro-litter standardized, harmonized and validated datasets 2011/2020 v2021. (2023). https://doi.org/10.13120/q6t1-2r39","M. D. Wilkinson, M. Dumontier, Ij. J. Aalbersberg, G. Appleton, M. Axton, A. Baak, N. Blomberg, J. W. Boiten, L. B. da Silva Santos, P. E. Bourne, J. Bouwman, A. J. Brookes, T. Clark, M. Crosas, I. Dillo, O. Dumon, S. Edmunds, C. T. Evelo, R. Finkers, A. Gonzalez-Beltran, A. J. G. Gray, P. Groth, C. Goble, J. S. Grethe, J. Heringa, P. A. C. t Hoen, R. Hooft, T. Kuhn, R. Kok, J. Kok, S. J. Lusher, M. E. Martone, A. Mons, A. L. Packer, B. Persson, P. Rocca-Serra, M. Roos, R. van Schaik, S. A. Sansone, E. Schultes, T. Sengstag, T. Slater, G. Strawn, M. A. Swertz, M. Thompson, J. Van Der Lei, E. Van Mulligen, J. Velterop, A. Waagmeester, P. Wittenburg, K. Wolstencroft, J. Zhao, & B. Mons, The FAIR Guiding Principles for scientific data management and stewardship. Scientific Data, 3 (2016) 1–9. https://doi.org/10.1038/sdata.2016.18","NOAA/ National Centers for Environmental Information (NCEI), Microplastics Database. (2022)","K. L. Law, S. Morét-Ferguson, N. A. Maximenko, G. Proskurowski, E. E. Peacock, J. Hafner, & C. M. Reddy, Plastic accumulation in the North Atlantic subtropical gyre. Science, 329 (2010). https://doi.org/10.1126/science.1192321","K. L. Law, S. E. Morét-Ferguson, D. S. Goodwin, E. R. Zettler, E. Deforce, T. Kukulka, & G. Proskurowski, Distribution of surface plastic debris in the eastern pacific ocean from an 11-year data set. Environmental Science and Technology, 48 (2014). https://doi.org/10.1021/es4053076","W. P. de Haan, A. Sanchez-Vidal, & M. Canals, Floating microplastics and aggregate formation in the Western Mediterranean Sea. Marine Pollution Bulletin, 140 (2019). https://doi.org/10.1016/j.marpolbul.2019.01.053","M. C. Goldstein, A. J. Titmus, & M. Ford, Scales of spatial heterogeneity of plastic marine debris in the northeast Pacific Ocean. PLoS ONE, 8 (2013). https://doi.org/10.1371/journal.pone.0080020","G. Suaria, C. G. Avio, A. Mineo, G. L. Lattin, M. G. Magaldi, G. Belmonte, C. J. Moore, F. Regoli, & S. Aliani, The Mediterranean Plastic Soup: Synthetic polymers in Mediterranean surface waters. Scientific Reports, 6 (2016). https://doi.org/10.1038/srep37551","G. Suaria, V. Perold, J. R. Lee, F. Lebouard, S. Aliani, & P. G. Ryan, Floating macro- and microplastics around the Southern Ocean: Results from the Antarctic Circumnavigation Expedition. Environment International, 136 (2020). https://doi.org/10.1016/j.envint.2020.105494","J. Reisser, J. Shaw, C. Wilcox, B. D. Hardesty, M. Proietti, M. Thums, & C. Pattiaratchi, Marine plastic pollution in waters around Australia: Characteristics, concentrations, and pathways. PLoS ONE, 8 (2013). https://doi.org/10.1371/journal.pone.0080466","T. Tanhua, S. B. Gutekunst, & A. Biastoch, A near-synoptic survey of ocean microplastic concentration along an around-the-world sailing race. PLoS ONE, 15 (2020). https://doi.org/10.1371/journal.pone.0243203","A. P. W. Barrows, S. E. Cathey, & C. W. Petersen, Marine environment microfiber contamination: Global patterns and the diversity of microparticle origins. Environmental Pollution, 237 (2018). https://doi.org/10.1016/j.envpol.2018.02.062","A. Isobe, T. Azuma, M. R. Cordova, A. Cózar, F. Galgani, R. Hagita, L. D. Kanhai, K. Imai, S. Iwasaki, S. Kako, N. Kozlovskii, A. L. Lusher, S. A. Mason, Y. Michida, T. Mituhasi, Y. Morii, T. Mukai, A. Popova, K. Shimizu, T. Tokai, K. Uchida, M. Yagi, & W. Zhang, A multilevel dataset of microplastic abundance in the world's upper ocean and the Laurentian Great Lakes. Microplastics and Nanoplastics, 1 (2021) 1–14. https://doi.org/10.1186/s43591-021-00013-z","IMO/FAO/UNESCO-IOC/UNIDO/WMO/IAEA/UN/UNEP/UNDP/ISA, Guidelines for the monitoring and assessment of plastic litter in the ocean: GESAMP Joint Group of Experts on the Scientific Aspects of Marine Environmental Protection (2019)","Y. Michida, S. Chavanich, S. Chiba, M. R. Cordova, A. Cozsar Cabanas, F. Glagani, P. Hagmann, H. Hinata, A. Isobe, P. Kershaw, N. Kozlovskii, D. Li, A. L. Lusher, E. Marti, S. A. Mason, J. Mu, H. Saito, W. J. Shim, A. D. Syakti, H. Takada, R. Thompson, T. Tokai, K. Uchida, K. Vasilenko, & J. Wang, Guidelines for Harmonizing Ocean Surface Microplastic Monitoring Methods. Ministry of the Environment Japan, (2020) 71","ICES, Manual for the International Bottom Trawl Surveys (Copenhagen, 2012)","MEDITS Working Group, MEDITS - Handbook. Version n.9 (2017)","ICES, Manual for the International Bottom Trawl Surveys. Series of ICES Survey Protocols. SISP 1-IBTS VIII. Series of ICES Survey Protocols.SIPS 1-IBTS VIII, (2012). https://doi.org/10.17895/ices.pub","ICES, SISP 2 Manual for the Midwater Ring Net sampling during IBTS Q1 (2013)","M. Bergmann, M. B. Tekman, & L. Gutow, LITTERBASE: An Online Portal for Marine Litter and Microplastics and Their Implications for Marine Life. Fate Impact Microplastics Mar. Ecosyst. (2017). https://doi.org/10.1016/b978-0-12-812271-6.00104-6"]}

Published
2023
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16. Organic Carbon Origin, Benthic Faunal Consumption, and Burial in Sediments of Northern Atlantic and Arctic Fjords (60–81°N)

Author

Włodarska‐kowalczuk, Maria, Mazurkiewicz, Mikołaj, Górska, Barbara, Michel, Loic, Jankowska, Emilia, Zaborska, Agata, Włodarska‐kowalczuk, Maria, Mazurkiewicz, Mikołaj, Górska, Barbara, Michel, Loic, Jankowska, Emilia, and Zaborska, Agata

Abstract

Fjords have been recently recognized as hotspots of organic carbon (Corg) sequestration in marine sediments. This study aims to identify regional and local drivers of variability of Corg burial in north Atlantic and Arctic fjords. We provide a comparative quantification of Corg, δ13C, photosynthetic pigments content, benthic biomass, consumption, Corg accumulation and burial rates in sediments in six fjords (60 to 810N). Higher sediment Corg content in southern Norway reflected longer phytoplankton growth season and higher productivity. Higher contributions of terrestrial Corg were noted in temperate/southern Norway (dense land vegetation and high precipitation) and Arctic/Svalbard (glacial erosion) than in subarctic/northern Norway locations. Benthic biomass and carbon consumption were best correlated to δ13C and photosynthetic pigments content indicating control by quality rather than quantity of available food. Benthic faunal consumption did not seem to affect the variability in Corg burial. Regional environmental factors (water temperature, latitude) combined with local factors (Corg, grain size, pigment concentration) explained 94 % of Corg burial variability. Based on the present study and literature data on Corg content, origin and burial rates, the fjords were classified into four categories: temperate, subarctic, Arctic with and without glaciers. The variability in marine productivity, terrestrial inflows and carbon sequestration in fjords must be considered for global estimates of their role in blue carbon storage and for building scenarios of future changes in the course of climate warming.

Published
2019
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17. Gammarus (Amphipoda) species competitive exclusion or coexistence as a result of climate change in the Arctic?

Author

WĘSŁAWSKI, Jan Marcin, LEGEŻYŃSKA, Joanna, KOTWICKI, Lech, MAZURKIEWICZ, Mikołaj, and OLENIN, Sergej

Abstract

The coexistence of two congeneric amphipods, boreal Gammarus oceanicus, and arctic G. setosus, was studied during the summer seasons of 2017-2019 in the region of Isfjorden, Forlandsundet, and Prins Karl Forland island in the west-central part of the Svalbard archipelago (Arctic). Across the study area species distribution often overlapped, but the domination patterns mirrored environmental conditions preferred by each species. Both species, however, were able to survive in suboptimal conditions. On a small spatial scale (in one sample) the species were separated, which may suggest an antagonistic relationship between them. The ongoing changes in the environment of Svalbard will likely affect these two species differently. The increasing intrusion of Atlantic waters will probably favor the further expansion of G. oceanicus along the Svalbard coasts. This will be due to the gradual advance of the existing population, as an influx of individuals from the Nordic seas seems unlikely. G. setosus will remain the dominant species in cold-water areas such as the inner fjords and the northeastern coast of Svalbard and may find new suitable habitats in lagoons or estuaries fed by melting glaciers. Despite predicted changes in the distribution range of both species, their future coexistence should still be possible due to the wide range of environmental tolerance and the heterogeneity of the Svalbard coastal habitats. [ABSTRACT FROM AUTHOR]

Published
2021
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