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Phytoplankton dynamics in relation to physicochemical conditions in large, stratified Lake Charzykowskie (Northern Poland) Cover

Phytoplankton dynamics in relation to physicochemical conditions in large, stratified Lake Charzykowskie (Northern Poland)

Open Access
|Sep 2017

Figures & Tables

Figure 1

Lake Charzykowskie – the map and the numbers of sampling sites
Lake Charzykowskie – the map and the numbers of sampling sites

Figure 2

Percentage contribution of taxonomic groups to the total biomass of phytoplankton in Lake Charzykowskie in 2014 (a) and 2015 (b)
Percentage contribution of taxonomic groups to the total biomass of phytoplankton in Lake Charzykowskie in 2014 (a) and 2015 (b)

Figure 3

Changes in the biomass (mg l-1) and chlorophyll a concentration (µg l-1) in the phytoplankton of Lake Charzykowskie in 2014 (a) and 2015 (b); biomass – bar, chlorophyll a – line
Changes in the biomass (mg l-1) and chlorophyll a concentration (µg l-1) in the phytoplankton of Lake Charzykowskie in 2014 (a) and 2015 (b); biomass – bar, chlorophyll a – line

Figure 4

Ordination plot of canonical correspondence analysis (CCA) for the biomass of phytoplankton groups and environmental parameters in Lake Charzykowskie in 2014-2015. The first axis accounts for 31.221% of the total data variance, the second axis – for 14.130%.
Ordination plot of canonical correspondence analysis (CCA) for the biomass of phytoplankton groups and environmental parameters in Lake Charzykowskie in 2014-2015. The first axis accounts for 31.221% of the total data variance, the second axis – for 14.130%.

Selected physicochemical parameters of water in Lake Charzykowskie in 2014-2015

parameter20142015
meanrange±SDmeanrange±SD
Secchi depth (m)2.81.9-5.51.22.41.7-4.10.7
Dissolved oxygen (mg l-1)8.34.8-10.62.19.37.5-11.41.2
Water temperature (°C)20.015.4-25.03.618.415.0-21.32.7
pH8.06.7-8.50.67.96.8-8.50.6
Electrolytic conductivity (µS cm-1)329317-3489.3332302-35714.9
Chlorophyll a (µg l-1)25.412.27-78.3221.8012.442.9-21.315.26
TP (mg l-1)0.1010.015-0.3000.100.1490.045-0.4960.12
TN (mg l-1)3.451.65-5.251.23.490.33-8.732.07

Statistically significant values of Pearson correlation between environmental parameters and phytoplankton biomass (p≤0_05, bold p≤ 0_001)

WTSDECpHDON-NH4N-NO2N-NO3TNP-PO4Chl aDinoEugl
SD-0.5113
EC 0.4992
pH0.6326-0.5742
DO 0.5258
N-NH40.6409-0.4101 0.5970
N-NO2 0.5213 0.6334
N-NO3 -0.4384 -0.5323
TN -0.4358
P-PO, 0.3837
Chl a 0.4079 0.5159
Cyano -0.50170.3930-0.5295 -0.5646 0.3757
Crypto1-0.4153
Dino0.7098-0.4801 0.4615
Eugl 0.4925
Chryso 0.5305 0.7463
Bacill -0.3932
Chloro 0.5316 0.6312
B phyto0.6959-0.6359-0.38420.4268 0.4338 0.8959

Structural changes in phytoplankton of Lake Charzykowskie in 1947-2015

Date of studies AuthorsChl a (µg l-1)Biomass (µg l-1)Dominants and subdominantsStrategyFGsTraits of phytoplanktonTrophic status
1947(Cabejszek 1950) 0.72Aulacoseira granulataAphanizomenon HosaquaeMicrocystis aeruginosaRSSPH1LMdiatomaceous and cyanobacterialβ-mesotrophy
1954-1955(Solski 1962)4.5-73.5 ?eutrophy
1968(Szulkowska-Wojaczek 1978) 2.44Fragilaria crotonensisMicrocystis aeruginosaRPcyanobacterial and diatomaceouseutrophy
1976(Szulkowska-Wojaczek 1978) 1.26Microcystis aeruginosa Oscillatoria n.det.SLMcyanobacterial bloomeutrophy
1987-1990(Wiśniewska 1994)1.33-90.80.5-43.4Aulacoseira granulataCyclotella sp. div.Microcystis aeruginosaAphanizomenon flos-aquaeRCRSSP-LMH1diatomaceous and cyanobacterial bloomhypertrophy
1999(Wiśniewska 2000)4.2-28.30.06-10.4Fragilaria crotonensisCeratium hirundinellaAphanizomenon flos-aquaeMicrocystis aeruginosaRSSSPLMH1LMdiatoms, dinoflagellates, cyanobacteriaeutrophy
2004(Wiśniewska 2005)8.3-49.41.8-107.4Asterionella formosaFragilaria crotonensisCeratium hirundinellaAulacoseira granulataMicrocystis aeruginosaRRSRSCPLMHPLMdiatoms, dinoflagellates, cyanobacteriahypertrophy
2008(Luścińska & Wiśniewska 2012) 1.1-11.0Stephanodiscus neoastrea, S. alpinusAulacoseira islandicaCeratium hirundinellaAphanothece minutissimaCCSCSCPLMLdiatoms and dinoflagellatesmeso-eutrophy
2009(Luścińska & Wiśniewska 2012) 3.3-7.6Plagioselmis sp.Microcystis wesenbergiiCeratium hirundinellaCSSX2LMLMcryptophytes, cryptophytes, dinoflagellatesmeso-eutrophy
2014(Wiśniewska & Dembowska this article)2.27-78.320.3-37.82Stephanodiscus neoastrea, S. alpinusAulacoseira islandicaCeratium hirundinellaCSSCPLMdiatoms and dinoflagellatesmeso-eutrophy
2015 (Wiśniewska & Dembowska this article)2.9-21.310.5-11.3Plagioselmis sp.Microcystis wesenbergiiCeratium hirundinellaFragilaria crotonensisCSSRX2LMLMPcryptophytes, cyanobacteria, dinoflagellatesmeso-eutrophy

Main functional groups in Lake Charzykowskie and representative species in each group (after Reynolds et al_ 2002; Padisák et al_ 2009) FG Representative species

FGRepresentative speciesPhysiological characteristics
BAulacoseira islandica Stephanodiscus neoastraeaMixed, mesotrophic small- and medium-sized lakes, sensitive to the onset of stratification, adapted to low light, sensitive to pH increase, Si depletion, stratification
CAsterionella formosaMixed, eutrophic small- and medium-sized lakes with species sensitive to the onset of stratification, sensitive to Si depletion
oFragilaria crotonensis Aulacoseira granulata A. granulata var. angustissima Staurastrum gracile S. chaetoceras Staurastrum sp.Eutrophic epilimnia, tolerant of carbon dioxide depletion, more eutrophic waters, sensitive to Si depletion, stratification
LMMicrocystis sp. Ceratium hirundinella C. furcoidesSummer epilimnia in eutrophic lakes, low light and very low C tolerant, sensitive to mixing and poor stratification
H2Gloeotrichia echinulata Anabaena lemmermaniiOligo-mesotrophic, deep, stratified lakes, with good light conditions, tolerant to low nitrogen, sensitive to mixing, poor light
HIAphanizomenon spp. Dolichospermum spiroidesEutrophic, both stratified and shallow lakes with low nitrogen and low carbon, sensitive to mixing, poor light and low phosphorus
X2PlagioselmisShallow, clear, mixed layers in meso-eutrophic lakes, tolerance to stratification, sensitive to mixing and filter-feeding grazers, reduced grazing leads to high relative biomass
GEudorina VolvoxNutrient-rich conditions in stagnant water columns, small eutrophic lakes and very stable phases in larger river-fed basins and storage reservoirs
K (L)?Aphanothece AphanocapsaAphanothece and Aphanocapsa colonies are often found late summer in epilimnion of oligotrophic, deep lakes
DOI: https://doi.org/10.1515/ohs-2017-0028 | Journal eISSN: 1897-3191 | Journal ISSN: 1730-413X
Language: English
Page range: 260 - 270
Submitted on: Nov 13, 2016
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Accepted on: Dec 29, 2016
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Published on: Sep 27, 2017
Published by: University of Gdańsk
In partnership with: Paradigm Publishing Services
Publication frequency: 4 issues per year

© 2017 Marzenna Wiśniewska, Ewa A. Dembowska, published by University of Gdańsk
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 License.