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. 2020 Jun 12;31:105856. doi: 10.1016/j.dib.2020.105856

Data on distribution, demographic structure and grazing of the dominant mesozooplankton species in the Yenisei estuary and adjacent shelf in early summer

AV Drits 1,, AF Pasternak 1, EG Arashkevich 1, SG Poyarkov 1, MV Flint 1
PMCID: PMC7317680  PMID: 32613042

Abstract

The data article refers to the paper “Distribution and grazing of the dominant mesozooplankton species in the Yenisei estuary and adjacent shelf in early summer (July 2016)” (Drits et al., 2020). The data were collected along quasi-longitudinal transect “Yenisei estuary – Kara Sea shelf” on 24–28 July 2016. Here we present data on the spatial and vertical distribution, demographic structure and gut pigment content of the dominant zooplankton species as well as the grazing impact on autotrophic phytoplankton in the three distinguished zones: freshwater zone, frontal zone of the Yenisei plume and marine shelf zone. The related article (Drits et al., 2020) considers the structure and functioning of zooplankton community in relation to environmental characteristics such as temperature, salinity, phytoplankton abundance, timing of ice retreat. Information presented in this article can be used by marine biologists for studies of structure and functioning of estuarine pelagic communities, ecology of zooplankton in the Siberian seas. Besides the data could provide a baseline for the assessment of the ecological role played by climate change events (e.g., increased precipitation, permafrost thawing, elevated river discharge) on the Arctic ecosystems.

Keywords: Kara sea, Yenisei estuary, Zooplankton, Distribution, Herbivorous feeding, Grazing impact


Specifications table

Subject Biology
Specific subject area Zooplankton ecology
Type of data Tables Figures
How data were acquired CTD probe (Seabird Electronics SBE-32), Juday closing plankton net (0.1 m2 mouth area, 180 µm mesh size), stereomicroscope Leica MZ6, Trilogy Laboratory Fluorometer Turner Designs
Data format Raw Analyzed
Parameters for data collection Samples of zooplankton were collected considering data on hydrographic (salinity, temperature) and biological (chlorophyll fluorescence) distribution patterns. Live samples were treated for gut fluorescence analysis immediately after collection. Preserved samples were analyzed for determination of zooplankton abundance and biomass within a few months.
Description of data collection Mesozooplankton was sampled by vertical tows using a Juday closing plankton net. Zooplankton were identified, staged, measured and counted in the laboratory under a stereomicroscope. Gut pigment content of zooplankters was measured by a fluorometric procedure.
Data source location Data were collected along a quasi- longitudinal transect “Yenisei estuary – Kara Sea shelf” 24 stations between 75° 55′ and 71° 50′ N.
Data accessibility With the article
Related research article A.V. Drits, A.F. Pasternak, E.G. Arashkevich, S.G. Poyarkov, M.V. Flint.
Distribution and grazing of the dominant mesozooplankton species in the Yenisei estuary and adjacent shelf in early summer (July 2016).
Continental Shelf Research, 2020, 201, 104-133.

Value of the data

  • There is virtually no data on distribution and demographic structure of zooplankton in the Yenisei estuary and adjacent shelf in the early summer (soon after the Yenisei discharge maximum). Our data fill this gap.

  • The data are among the few that describe zooplankton feeding and grazing impact on autotrophic phytoplankton in the Yenisei estuary and adjacent Kara sea shelf.

  • The data can be used to study the impact of seasonal changes and river run-off in the Arctic shelf seas on the structure and grazing of zooplankton as well as when studying other estuarine pelagic communities.

  • The data form a necessary step to assess the effects of climate change in the area of Yenisei influence.

1. Data

The data were obtained at 24 sampling stations investigating the distribution and grazing of dominant mesozooplankton species in the Yenisei estuary and adjacent Kara sea shelf in early summer (July 2016). The environmental characteristics of the stations are given in Table 1. The freshwater zone (sts. 5345, 5344, 5343, 5342), frontal zone of the Yenisei plume (sts. 5340, 5339, 5337, 5335, 5333, 5350, 5351) and marine shelf zone outside the plume (5352 and 5353) were distinguished according to salinity and temperature characteristics.

Table 1.

Stations coordinates, depth (m), surface and bottom salinity (Ssur, Sbot), surface and bottom temperature (Tsur °C, Tbot °C).

Station Latitude, N Longitude, E Depth Ssur Sbot Tsur Tbot
5333 74°15,0′ 79°10,0′ 30 8.3 30.3 11.2 −1.2
5333_2 74°15,1′ 79°09,8′ 30 7.3 31.0 11.1 −1.4
5334 74°00,4′ 79°23,0′ 30 6.4 31.1 10.2 −1.4
5335 73°45,7′ 79°36,6′ 30 5.6 31.9 11.4 −1.4
5335_2 73°45,9′ 79°36,1′ 30 7.4 31.7 11.5 −1.4
5336 73°33,5′ 79°47,4′ 38 7.4 32.7 11.3 −1.4
5337 73°18,4′ 79°50,9′ 32 7.1 31.4 11.8 −1.4
5337_2 73°18,5′ 79°50,8′ 32 7.7 32.0 11.2 −1.5
5338 73°03,3′ 79°55,2′ 25 6.8 31.0 11.9 −1.4
5339 72°49,0′ 80°00,0′ 23 4.9 29.0 12.9 −1.2
5339_2 72°49,0′ 79°59,9′ 23 5.4 31.1 12.7 −1.4
5340 72°35,9′ 80°25,0′ 15 5.3 27.6 12.5 −0.3
5340_2 72°35,8′ 80°25,4′ 15 6.0 28.0 12.6 −0.4
5342 72°12,4′ 80°50,3′ 12 1.4 26.1 15.6 −0.2
5342_2 72°12,4′ 80°50,0 12 0.9 27.9 15.6 −0.2
5343 72°05,6′ 81°28,9′ 10 1.6 20.9 15.2 6
5344 71°52,0′ 82°11,9′ 10 0.5 1.3 17.1 16.1
5344_2 71°52,0′ 82°12,0′ 10 0.6 1.4 16.6 15.9
5345 71°50,4′ 082°54,0′ 21 0.4 21.4 17.5 6.3
5350 74°52,0′ 078°26,9′ 22 9.9 29.4 11.6 −1.4
5351 75°12,2′ 078°21,1 43 14.2 32.5 11.1 −1.5
5352 75°16,9′ 078°18,5′ 40 29.6 33.1 6.5 −1.4
5353 75°55,0′ 078°34,0′ 63 31.4 33.7 3.7 −0.9

Distribution of the biomass of the dominant zooplankton at the sampled stations is presented in Table 2. Cladocera and mysids dominated zooplankton biomass in the freshwater zone. In the Yenisei plume zone, Limnocalanus macrurus dominated zooplankton biomass while C. glacialis dominated in the marine shelf zone (Table 2).

Table 2.

Biomass (mg dry weight m−3) of the dominant components of zooplankton along the transect “Yenisei estuary – Kara Sea shelf”.

Station Species
Calanus glacialis Pseudocalanus spp. Limnocalanus macrurus Mysis oculata Bosmina sp. Daphnia spp. Oikopleura vanhoeffeni Others
5333 12.6 8.5 6.4 3.0 0.0 0.0 1.4 4.7
5333_2 51.9 5.3 7.9 0.0 0.0 0.0 16.0 5.2
5334 13.5 9.6 24.9 0.0 0.0 0.0 25.0 4.6
5335 38.9 8.6 7.7 2.5 0.0 0.0 15.8 6.7
5335_2 5.6 17.5 31.4 0.0 0.0 0.0 15.0 1.6
5336 3.8 10.2 33.1 0.0 0.0 0.0 16.8 3.7
5337 2.6 10.7 17.7 3.2 0.0 0.0 6.8 3.4
5337_2 8.5 18.7 12.7 3.2 0.0 0.0 17.0 6.8
5338 8.6 8.2 1.1 12.6 0.0 0.0 4.5 2.7
5339 1.3 14.7 43.1 0.0 0.0 0.0 0.0 5.3
5339_2 0.0 17.5 9.9 21.8 0.0 0.0 0.0 5.4
5340 0.0 18.5 79.3 0.0 0.0 0.0 0.0 2.2
5340_2 0.0 5.1 38.9 0.0 0.0 0.0 0.0 2.2
5342 0.0 3.6 6.0 0.0 0.7 0.8 0.0 3.4
5342_2 3.4 5.5 11.9 17.0 2.3 2.2 0.0 8.3
5343 0.0 0.0 1.2 0.0 0.8 0.7 0.0 2.7
5344 0.0 0.0 0.0 0.0 10.4 12.6 0.0 5.3
5344_2 0.0 0.0 0.0 1.1 2.8 3.0 0.0 1.3
5345 0.0 0.0 0.0 16.8 3.7 4.1 0.0 2.2
5350 3.2 3.7 4.7 0.0 0.0 0.0 0.0 0.4
5351 17.3 5.0 0.0 0.0 0.0 0.0 6.0 5.0
5352 3.4 5.3 0.0 0.0 0.0 0.0 0.2 3.8
5353 17.6 1.9 0.0 0.0 0.0 0.0 2.0 5.5

Data on the vertical distribution of the dominant zooplankton are presented in Table 3. In the freshwater zone, the dominant zooplankton group, Cladocera, concentrated in the upper water layer. In the Yenisei plume, mesozooplankton avoided the upper freshened layer with Calanus glacialis and L. macrurus concentrating in the pycnoline layer. Oikopleura vanhoeffeni was observed only in the deeper layer, while in the marine shelf zone, they inhabited the upper mixed layer (Table 3). Horizontal and vertical distribution of the dominant zooplankton species was analyzed in relation to temperature, salinity, and Chl a concentration using Canonical correspondence analysis (CCA) [1].

Table 3.

Vertical distribution of abundance (ind m−3) of dominant zooplankton species. The layers below, within and above the pycnocline determined according to the CTD profiles were sampled.

Station Layer, m Cladocera Calanus glacialis Pseudocalanus spp. Limnocalanus macrurus Oikopleura vanhoeffeni
5333_2 0–5 0 0 102 0 0
5–10 0 1914 1524 276 6
10–28 0 52 1344 4 32
5335_2 0–5 0 4 124 0 0
5–10 0 234 1188 2 2
10–28 0 13 3431 294 16
5337_2 0–6 0 0 211 0 0
6–12 0 208 5514 215 2
12–29 0 24 2055 47 29
5339_2 0–5 0 0 540 12 0
5–19 0 11 2253 237 0
5340_2 5–0 0 0 58 16 0
5–12 0 0 930 400 0
5342_2 0–6 7320 0 0 0 0
6–11 550 0 1670 47 0
5345 0–10 12,980 0 0 0 0
10–18 350 0 0 0 0
5350 0–5 0 6 452 2 0
5–10 0 124 1508 82 2
10–18 0 20 538 8 13
5351 0–10 0 302 320 0 49
10–38 0 384 1417 0 4
5352 0–10 0 4 7 0 662
10–37 0 116 1648 0 2
5353 0–20 0 185 1054 0 155
20–58 720 417 0 4

Data on the demographic structure/size structure of the dominant zooplankters are given in Table 4. Dominance of the younger copepodites of Calanus glacialis and Pseudocalanus spp, as well as small size Oikopleura vanhoeffeni was noted at the marine shelf stations. The population of Limnocalanus macrurus consisted of adult specimens with almost equal numbers of females and males.

Table 4.

Demogaphic structure of the dominant zooplankton species. Abundance (ind m−3) of distinguished copepod age stages and larvacean size groups (trunk length, mm) are given.

Station Calanus glacialis
Pseudocalanus spp.
Limnocalanus macrurus
Oikopleura vanhoeffeni
CI CII CIII CIV CV CI-CIV CV Fem Fem Male <1mm 1–6 mm
5333 1 2 30 62 9 1712 76 15 24 14 1 1
5333_2 5 0 46 280 67 975 112 21 144 132 1 25
5334 1 2 36 52 0 962 151 60 91 56 1 23
5335 1 0 42 218 21 874 152 64 26 19 0 18
5335_2 5 3 14 26 5 1997 458 104 165 129 1 17
5336 0 0 9 7 5 990 234 38 119 76 0 14
5337 1 1 6 8 3 911 268 57 53 54 0 7
5337_2 0 0 6 46 4 1294 595 36 44 27 0 27
5338 1 1 13 45 6 1087 196 21 4 3 0 10
5339 0 0 0 0 0 1462 514 22 134 124 0 0
5339_2 0 0 0 0 0 872 994 20 52 27 0 0
5340 0 0 0 0 0 705 1069 3 244 233 0 0
5340_2 0 0 0 0 0 300 239 0 275 125 0 0
5342 0 0 0 0 0 361 107 0 18 17 0 0
5342_2 0 0 0 0 0 552 187 30 70 68 0 0
5350 5 21 13 3 5 733 41 8 0 0 0 13
5351 119 127 80 35 9 970 110 30 0 0 42 7
5352 29 34 12 4 2 983 152 18 0 0 196 0
5353 223 169 82 43 4 582 37 0 0 0 154 2

Gut pigment content of copepods depended on chlorophyll concentration in the layer of inhabitance (Fig. 1). A significant correlation between gut pigment content and Chl a concentration was found for all copepods but the correlation coefficient was very low for L. macrurus.

Fig. 1.

Fig 1

Gut pigment content (G) in dominant zooplankters vs chlorophyll a concentration (Chl a). L.m. – Limnocalanus macrurus, Ps. spp. – Pseudocalanus spp. CII-CIV, C. g. – Calanus glacialis.

In Oikopleura vanhoeffeni, gut pigment content depended significantly of the weight of the animals (Fig. 2).

Fig. 2.

Fig 2

Dependence of Oikopleura vanhoeffeni gut pigment content (G, ng pigment ind−1) on dry weight (DW, mg ind−1).

Zooplankton grazing on phytoplankton was calculated on the basis of measured gut pigment content of the dominant species and abundance of zooplankters in the sampled water layers (Table 5). The most important grazers were cladocerans (in the freshwater zone) and Calanus glacialis (in the Yenisei plume zone).

Table 5.

Grazing impact on autotrophic phytoplankton (mg Chl a m−2 day−1) by the populations of the dominant zooplankton species.

Station Layer, m Cladocera Calanus glacialis Pseudocalanus spp. Limnocalanus macrurus Oikopleura vanhoeffeni
5333 0–28 0 0.57 0.08 0.004 0
5333_2 0–5 0 0 0.004 0 0
5–10 0 2.92 0.11 0.02 0
10–28 0 0.01 0.01 0.1 0.26
5334 0–27 0 0.51 0.09 0.03 0
5335 0–28 0 3.54 0.65 0.04 0
5335_2 0–5 0 0 0.003 0 0
5–10 0 0.04 0.04 0.008 0.002
10–28 0 0.006 0.08 0.03 0.22
5336 0–35 0 0.04 0.16 0.08 0
5337 0–29 0 0.03 0.08 0.03 0
5337_2 0–6 0 0 0.007 0 0
6–12 0 0.05 0.22 0.008 0
12–29 0 0.014 0.18 0.006 0.18
5338 0–22 0 0.61 0.18 0 0
5339 0–20 0 0 0.92 0.13 0
5339_2 0–5 0 0 0 0 0
5–19 0 0 0.03 0.012 0
5340 0–12 0 0 0.38 0.42 0
5340_2 0–12 0 0 0.06 0.8 0
5342_2 0–6 0.93 0 0 0.01 0
5344 0–7 3.8 0 0 0 0
5345 0–10 3.03 0 0 0 0
5351 0–10 0 0.03 0.14 0 0.04
10–38 0 0.05 0.14 0 0.05
5353 0–20 0 0.017 0.03 0 0.004
20–58 0 0.42 0.015 0 0.02

2. Experimental design, materials and methods

2.1. Collection and processing of samples

The material was collected during cruise # 66 of the RV “Akademik Mstislav Keldysh” to the Kara Sea in July 2016. A quasi-longitudinaltransect was sampled in the Yenisei estuary and adjacent shelf (Fig. 3). At first, the transect was sampled from 74°15′ N to 71° 50′ N on 24–25 July. Based on the obtained salinity and temperature data, several stations were selected and repeated along the reversed transect from 71° 50′ N to 76° N on 26–28 July. The coordinates of the sampling stations are in Tables 1. Data on temperature and salinity were obtained with a CTD probe (Seabird Electronics SBE-32). Mesozooplankton was sampled using a Juday closing net (0.1 m2 mouth area, 180 µm mesh size). Two layers were sampled at most of the stations along the SN transect, below and above the pycnocline, which was determined according to the CTD profiles. Additionally, we sampled the pycnocline layer at four of the reversed transect stations. For determination of zooplankton abundance and biomass, samples were immediately preserved in 4% borax-buffered formalin. Zooplankton were identified, staged, measured and counted in the laboratory under a stereomicroscope. For determination of zooplankton abundance and biomass, samples were immediately preserved in 4% borax-buffered formalin. Zooplankton were identified, staged, measured and counted in the laboratory under a stereomicroscope. Not numerous large specimens (the older stages of Calanus spp., Limnocalanus macrurus, Oikopleura vanhoeffeni and Chaetognatha) were counted in the whole samples, while more numerous forms were counted in subsamples so as not less than 50 specimens were recorded. Most taxonomic groups including Copepoda, Cladocera, Pteropoda, Chaetognatha, Larvacea, Mysidacaea were identified to the species/genus level. Prosome length was used to distinguish the closely related copepod species Calanus finmarchicus and C. glacialis according to [2]. For Calanus and Limnocalanus, all copepodite stages were distinguished. For Pseudocalanus spp. copepodites CI to CIV were pooled. The wet weight (WW) of each species was calculated using nomograms [3]. These tables (www.twirpx.com/file/1588162/) allow the calculation of biovolume/wet weight of aquatic organisms based on their body shape and length. Dry weight (DW) of crustacean plankton was estimated as 0.16 WW [4], DW of chaetognaths was calculated according to [5], larvaceans – to [6].

Fig. 3.

Fig 3

Map of the study area: location of the transect is indicated with a bar.

2.2. Feeding of zooplankton

Feeding rates of the dominant species (Calanus glacialis, Limnocalanus macrurus, Pseudocalanus spp., Bosmina sp., Daphnia spp., Oikopleura vanhoeffeni) were assessed with the gut fluorescence method [7]. To measure gut pigment content, 1 to 40 animals per replicate, depending on size/stage, were picked with forceps and placed in test tubes with 3 ml of 90% acetone. Two to five replicates for each species/stage were analyzed. Pigments were extracted for 24 h at 5 °C in the dark. Chl a and phaeopigment were measured by a standard fluorometric procedure [8] with a Trilogy Laboratory Fluorometer (Turner Designs).

2.3. Zooplankton grazing impact

Grazing impact of each of the dominant species (mg Chl a m−2 day−1) was estimated using the mean individual daily ingestion rates (ng Chl a ind−1 d−1) and the abundance of the given species (ind m−2).

Declaration of Competing Interest

None.

Acknowledgements

This work was performed in the framework of the state assignment of Ministry of Science and Higher Education of the Russian Federation (theme № 0149–2019–0008, field work, processing and identification of zooplankton) and supported by the Russian Foundation for Basic Research (grants 18–05–60069, processing and analysis of environmental data, preparation of the manuscript, analysis of zooplankton distribution; 19–04–00322, analysis of zooplankton feeding; 19–05–00022, analysis of zooplankton grazing pressure).

Footnotes

Supplementary material associated with this article can be found, in the online version, at doi:10.1016/j.dib.2020.105856.

Appendix. Supplementary materials

mmc1.xml (348B, xml)

References

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Associated Data

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Supplementary Materials

mmc1.xml (348B, xml)

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