Elena M. Bezzubova

Mrs. Elena M. Bezzubova

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Research Focus & Metrics

Academic Career Length

9Years (2018-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 January 2020 in Oceanology
Verified
Journal Article
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EBElena M. Bezzubova
Elena M. Bezzubova
ASA. M. Seliverstova
A. M. Seliverstova
IZI. A. Zamyatin
I. A. Zamyatin
NRN. D. Romanova
N. D. Romanova
The present study examined the hydrochemical and biological parameters influencing the spatial distribution of bacterioplankton in the Laptev Sea and the East Siberian Sea shelf regions affected by the Khatanga, Indigirka and Kolyma rivers runoff during September 2017. The highest bacterial abundance and the amount of actively respiring bacteria were determined in rivers delta and in surface water along the edge of continental shelf. Despite the expectations based on previous studies salinity was not the determining factor affecting spatial distribution and activity of bacterioplankton. Bacterial abundance and biomass were significantly and positively correlated with chlorophyll “a” and pheophytin content.

1 June 2022 in Oceanology
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Journal Article
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NRN. D. Romanova
N. D. Romanova
MBM. A. Boltenkova
M. A. Boltenkova
APA. A. Polukhin
A. A. Polukhin
EBElena M. Bezzubova
Elena M. Bezzubova
SSS. A. Shchuka
S. A. Shchuka
Analysis of the distribution of abundance and activity of bacterioplankton in the estuary area of the Ob River in July 2016 and September 2013, as well as environmental factors, made it possible to distinguish between riverine, brackish water, and marine zones. In summer, the abundance of bacterioplankton varied from 2604 ± 436 × 103 cells/mL in brackish waters to 468 ± 91 × 103 cells/mL in seawater. The average values of bacterial production in waters with a salinity of less than 8 and more than 22 PSU were 17.43 and 4.91 mgC m–3 day–1, respectively. In autumn, the bacterial abundance decreased towards the sea from 1289 ± 385 × 103 cells/mL in freshwaters to 85 ± 37 × 103 cells/mL in the offshore part; the value of production decreased by more than an order of magnitude. With an increase in salinity, the proportion of cells with active electron transport chain in the abundance of bacterioplankton decreased from 5.8 to 0.6%. Thus, the distribution of river runoff, marked by salinity, proved to be the main factor affecting the spatial distribution and activity of bacterioplankton. However, the mechanism of such regulation remains unclear.

1 May 2018 in Oceanology
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EBElena M. Bezzubova
Elena M. Bezzubova
ADA. V. Drits
A. V. Drits
SMSergey A. Mosharov
Sergey A. Mosharov
The present work aimed to study the influence of mercuric chloride (HgCl2) on pigment content (chlorophyll aand pheophytin) in sediment traps on the basis of experimental data. The marine microalgal...

27 January 2024 in Polar Biology
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Journal Article
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EBElena M. Bezzubova
Elena M. Bezzubova
NRN. D. Romanova
N. D. Romanova
ASA. S. Shchuka
A. S. Shchuka
SASeliverstova Anna
Seliverstova Anna
NPN. A. Plotnikov
N. A. Plotnikov
AVAlexandra Volodina
Alexandra Volodina

1 June 2020 in Data in Brief
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Journal Article
Open access
Nikolay V. LobusNikolay V. Lobus
Nikolay V. Lobus
EBElena M. Bezzubova
Elena M. Bezzubova
DLDaria A. Litvinyuk
Daria A. Litvinyuk
The biogeochemical role of zooplankton in the ocean is determined not only by life-long accumulation of chemical elements from the environment, but also by post-mortal transformation of carcasses chemical composition. The contribution of zooplankton carcasses to vertical flux of major and trace elements depends on sedimentation and remineralization rates of detrital particles. Carcasses decomposition rate during sinking from the upper to the deeper water layers determines the rapid recycling of chemical elements and depends on ambient temperature and microbial activity. This data set summarizes 21-day experiment in microcosms that simulates temperature conditions in the Arctic environment. The data show slow decomposition of copepod carcasses compared with initial material on days 14-21 of the experiment. In addition to visual evidence, we provide data on changes in bacterial abundance and biomass during the whole experimental period.