期刊论文详细信息
Aquatic Biosystems
Factors controlling bacteria and protists in selected Mazurian eutrophic lakes (North-Eastern Poland) during spring
Krystyna Kalinowska1  Adam Guśpiel2  Bartosz Kiersztyn2  Ryszard J Chróst2 
[1] Polish Academy of Sciences, Centre for Ecological Research, Hydrobiological Station, ul. Leśna 13, Mikołajki, 11-730, Poland
[2] Department of Microbial Ecology, Institute of Botany, Faculty of Biology, University of Warsaw, ul. Miecznikowa 1, Warsaw, 02-096, Poland
关键词: Eutrophic lakes;    Protists;    Metabolic activity;    Bacteria;   
Others  :  794183
DOI  :  10.1186/2046-9063-9-9
 received in 2013-01-02, accepted in 2013-03-28,  发布年份 2013
PDF
【 摘 要 】

Background

The bottom-up (food resources) and top-down (grazing pressure) controls, with other environmental parameters (water temperature, pH) are the main factors regulating the abundance and structure of microbial communities in aquatic ecosystems. It is still not definitively decided which of the two control mechanisms is more important. The significance of bottom-up versus top-down controls may alter with lake productivity and season. In oligo- and/or mesotrophic environments, the bottom-up control is mostly important in regulating bacterial abundances, while in eutrophic systems, the top-down control may be more significant.

Results

The abundance of bacteria, heterotrophic (HNF) and autotrophic (ANF) nanoflagellates and ciliates, as well as bacterial production (BP) and metabolically active cells of bacteria (CTC, NuCC, EST) were studied in eutrophic lakes (Mazurian Lake District, Poland) during spring. The studied lakes were characterized by high nanoflagellate (mean 17.36 ± 8.57 × 103 cells ml-1) and ciliate abundances (mean 59.9 ± 22.4 ind. ml-1) that were higher in the euphotic zone than in the bottom waters, with relatively low bacterial densities (4.76 ± 2.08 × 106 cells ml-1) that were lower in the euphotic zone compared to the profundal zone. Oligotrichida (Rimostrombidium spp.), Prostomatida (Urotricha spp.) and Scuticociliatida (Histiobalantium bodamicum) dominated in the euphotic zone, whereas oligotrichs Tintinnidium sp. and prostomatids Urotricha spp. were most numerous in the bottom waters. Among the staining methods used to examine bacterial cellular metabolic activity, the lowest percentage of active cells was recorded with the CTC (1.5–15.4%) and EST (2.7–14.2%) assay in contrast to the NuCC (28.8–97.3%) method.

Conclusions

In the euphotic zone, the bottom-up factors (TP and DOC concentrations) played a more important role than top-down control (grazing by protists) in regulating bacterial numbers and activity. None of the single analyzed factors controlled bacterial abundance in the bottom waters. The results of this study suggest that both control mechanisms, bottom-up and top-down, simultaneously regulated bacterial community and their activity in the profundal zone of the studied lakes during spring. In both lake water layers, food availability (algae, nanoflagellates) was probably the major factor determining ciliate abundance and their composition. In the bottom waters, both groups of protists appeared to be also influenced by oxygen, temperature, and total phosphorus.

【 授权许可】

   
2013 Kalinowska et al.; licensee BioMed Central Ltd.

【 预 览 】
附件列表
Files Size Format View
20140705063536341.pdf 1728KB PDF download
Figure 8. 105KB Image download
Figure 7. 132KB Image download
Figure 6. 68KB Image download
Figure 5. 96KB Image download
Figure 4. 65KB Image download
Figure 3. 73KB Image download
Figure 2. 136KB Image download
Figure 1. 65KB Image download
【 图 表 】

Figure 1.

Figure 2.

Figure 3.

Figure 4.

Figure 5.

Figure 6.

Figure 7.

Figure 8.

【 参考文献 】
  • [1]Šimek K, Macek M, Seda J, Vyhnálek V: Possible food chain relationships between bacterioplankton, protozoans and cladocerans in a reservoir. Int Revue ges Hydrobiol 1990, 75:583-596.
  • [2]Šimek K, Armengol J, Comerma M, Garcia J-C, Chrzanowski TH, Macek M, Nedoma J, Straškrabová V: Characteristics of protistan control of bacterial production in three reservoirs of different trophy. Int Rev Hydrobiol 1998, 83:485-494.
  • [3]Horňák K, Jezbera J, Šimek K: Bacterial single-cell activities along the nutrient availability gradient in a canyon-shaped reservoir: a seasonal study. Aquat Microb Ecol 2010, 60:215-225.
  • [4]Sommer U, Gliwicz ZM, Lampert W, Duncan A: The PEG-model of seasonal succession of planktonic events in fresh waters. Arch Hydrobiol 1986, 106:433-471.
  • [5]Zdanowski B: Variability of nitrogen and phosphorus contents and lake eutrophication. Pol Arch Hydrobiol 1982, 29:541-597.
  • [6]Lampert W, Fleckner W, Rai H, Taylor BE: Phytoplankton control by grazing zooplankton: a study on the spring clear-water phase. Limnol Oceanogr 1986, 31:478-490.
  • [7]Sommer U: Factors controlling the seasonal variation in phytoplankton species composition-a case study for a deep, nutrient rich lake. Prog Phycol Res 1987, 5:123-178.
  • [8]Auer B, Elzer U, Arndt H: Comparison of pelagic food webs in lakes along a trophic gradient and with seasonal aspects: influence of resource and predation. J Plankton Res 2004, 26:697-709.
  • [9]Weisse T, Müller H, Pinto-Coelho RM, Baldringer G: Response of microbial loop to the phytoplankton spring bloom in a large pre-alpine lake. Limnol Oceanogr 1990, 35:781-794.
  • [10]Müller H, Schöne A, Pinto-Coelho RM, Schweizer A, Weisse T: Seasonal succession of ciliates in Lake Constance. Microb Ecol 1991, 21:119-138.
  • [11]Mathes J, Arndt H: Annual cycle of protozooplankton (ciliates, flagellates and sarcodines) in relation to phyto- and metazooplankton in Lake Neumühler See (Mecklenburg, Germany). Arch Hydrobiol 1995, 134:337-358.
  • [12]Gajewski AJ, Chróst RJ: Microbial enzyme activities and phytoplankton and bacterial production in the pelagial of the Great Mazurian Lakes (North-Eastern Poland) during summer stratification. Ekol Pol 1995, 43:245-265.
  • [13]Chróst RJ, Siuda W: Microbial production, utilization, and enzymatic degradation of organic matter in the upper trophogenic layer in the pelagial zone of lakes along a eutrophication gradient. Limnol Oceanogr 2006, 51:749-762.
  • [14]Chróst RJ, Adamczewski T, Kalinowska K, Skowrońska A: Abundance and structure of microbial loop components (bacteria and protists) in lakes of different trophic status. J Microbiol Biotechnol 2009, 19:858-868.
  • [15]Beaver JR, Crisman TL: The trophic response of ciliated protozoans in freshwater lakes. Limnol Oceanogr 1982, 27:246-253.
  • [16]Auer B, Arndt H: Taxonomic composition and biomass of heterotrophic flagellates in relation to lake trophy and season. Freshwat Biol 2001, 46:959-972.
  • [17]Karabin A: Pelagic zooplankton (Rotatoria + Crustacea) variation in the process of lake eutrophication. I. Structural and quantitative features. Ekol Pol 1985, 33:567-616.
  • [18]Kiersztyn B, Siuda W, Chróst RJ: Microbial ectoenzyme activity: useful parameters for characterizing the trophic conditions of lakes. Pol J Environ Stud 2002, 11:367-373.
  • [19]Gajewski AJ, Chróst RJ, Siuda W: Bacterial lipolytic activity in an eutrophic lake. Arch Hydrobiol 1993, 128:107-126.
  • [20]Benett SJ, Sanders RW, Porter KG: Heterotrophic, autotrophic and mixotrophic nanoflagellates: seasonal abundances and bacterivory in a eutrophic lake. Limnol Oceanogr 1990, 35:1821-1832.
  • [21]Weisse T: The annual cycle of heterotrophic freshwater nanoflagellates: role of bottom-up versus top-down control. J Plankton Res 1991, 13:167-185.
  • [22]Carrias JF, Amblard C, Bourdier G: Seasonal dynamics and vertical distribution of planktonic ciliates and their relationship to microbial food resources in the oligomesotrophic Lake Pavin. Arch Hydrobiol 1998, 140:227-255.
  • [23]Šimek K, Hartman P, Nedoma J, Penthaler J, Springmann D, Vrba J, Psenner R: Community structure, picoplankton grazing and zooplankton control of heterotrophic nanoflagellates in a eutrophic reservoir during the summer phytoplankton maximum. Aquat Microb Ecol 1997, 12:49-63.
  • [24]Adamczewski T: Occurrence and morphological diversity of bacteria and their activity and biomass production in lakes of different trophic status. Warszawa, Poland: University of Warsaw, Department of Microbial Ecology; 2009. [PhD thesis]
  • [25]Sanders RW, Caron DA, Berninger UG: Relationships between bacteria and heterotrophic nanoplankton in marine and fresh waters: an inter-ecosystem comparison. Mar Ecol Prog Ser 1992, 86:1-14.
  • [26]Sanders RW, Porter KG, Bennett SJ, Debiase AE: Seasonal patterns of bacterivory by flagellates, ciliates, rotifers, and cladocerans in freshwater planktonic community. Limnol Oceanogr 1989, 34:673-687.
  • [27]Gasol JM, Vaqué D: Lack of coupling between heterotrophic nanoflagellates and bacteria: a common phenomenon across aquatic systems? Limnol Oceanogr 1993, 38:657-665.
  • [28]Gasol JM: A framework for the assessment of top-down vs. bottom-up control of heterotrophic nanoflagellates abundance. Mar Ecol Prog Ser 1994, 113:291-300.
  • [29]Koton-Czarnecka M, Chróst RJ: Measurements of protozoan grazing on bacteria by means of [3H-thymidine] – labeled natural assemblages of lake bacteria. Pol J Environ Stud 2002, 11:385-393.
  • [30]Sanders RW, Porter KG, McDonough R: Bacterivory by ciliates, microflagellates and mixotrophic algae: factor influencing particle ingestion. Eos 1985, 66:1314.
  • [31]Müller H, Weisse T: Laboratory and field observations on the scuticociliate Histiobalantium from the pelagic zone of Lake Constance, FRG. J Plankton Res 1994, 16:391-401.
  • [32]Gaedke U, Wickham SA: Ciliate dynamics in response to changing biotic and abiotic conditions in a large, deep lake (Lake Constance). Aquat Microb Ecol 2004, 34:247-261.
  • [33]Choi JW, Sherr BF, Sherr EB: Dead or alive? A large fraction of ETS-inactive marine bacterioplankton cells, as assessed by reduction of CTC, can become ETS-active with incubation and substrate addition. Aquat Microb Ecol 1999, 18:105-115.
  • [34]Berman T, Kaplan B, Chava S, Viner Y, Sherr BF, Sherr EB: Metabolically active bacteria in Lake Kinneret. Aquat Microb Ecol 2001, 23:213-224.
  • [35]Schumann R, Schiewer U, Karoten U, Rieling T: Viability of bacteria from different aquatic habitats. II. Cellular fluorescent markers for membrane integrity and metabolic activity. Aquat Microb Ecol 2003, 32:137-150.
  • [36]Smith EM, del Giorgio PA: Low fractions of active bacteria in natural aquatic communities? Aquat Microb Ecol 2003, 31:201-208.
  • [37]del Giorgio PA, Gasol JM, Vaqué D, Mura P, Agusti S, Duarte CM: Bacterioplankton community structure: protists control net production and the proportion of active bacteria in a coastal marine community. Limnol Oceanogr 1996, 41:1169-1179.
  • [38]Søndergaard M, Danielsen M: Active bacteria (CTC+) in temperate lakes: temporal and cross-system variations. J Plankton Res 2001, 23:1195-1206.
  • [39]Bernard L, Curties C, Servais P, Trousselier M, Petit M, Lebaron P: Relationships among bacterial cell size, productivity and genetic diversity in aquatic environments using cell sorting and flow cytometry. Microb Ecol 2000, 40:48-158.
  • [40]Chróst RJ, Adamczewski T, Kalinowska K, Skowrońska A: Inorganic phosphorus and nitrogen modify composition and diversity of microbial communities in water of mesotrophic lake. Pol J Microbiol 2009, 58:77-90.
  • [41]Koton-Czarnecka M, Chróst RJ: Protozoans prefer large and metabolically active bacteria. Pol J Environ Stud 2003, 12:325-334.
  • [42]Adamczewski T, Chróst RJ, Kalinowska K, Skowrońska A: Relationships between bacteria and heterotrophic nanoflagellates in lake water examined by different techniques controlling grazing pressure. Aquat Microb Ecol 2010, 60:203-213.
  • [43]Sherr BF, del Giorgio P, Sherr EB: Estimating abundance and single-cell characteristics of respiring bacteria via the redox dye CTC. Aquat Microb Ecol 1999, 18:117-131.
  • [44]del Giorgio PA, Scarborough G: Increase in the proportion of metabolically active bacteria along gradients of enrichment in freshwater and marine plankton: implications on estimates of bacterial growth and production rates. J Plankton Res 1995, 17:1905-1924.
  • [45]Tadonléké RD, Planas D, Lucotte M: Microbial food webs in boreal humic lakes and reservoirs: ciliates as a major factor related to the dynamics of the most active bacteria. Microb Ecol 2005, 49:325-341.
  • [46]Müller H, Geller W, Schöne A: Pelagic ciliates in Lake Constance: comparison of epilimnion and hypolimnion. Verh Internat Verein Limnol 1991, 24:846-849.
  • [47]Berdjeb L, Ghiglione J-F, Jacquet S: Bottom-up versus top-down of hypo- and epilimnion free-living bacterial community structure in two neighboring freshwater lakes. Appl Environ Microbiol 2011, 77:3591-3599.
  • [48]Jones RI: Advantages of diurnal vertical migrations to phytoplankton in sharply stratified, humic forest lakes. Arch Hydrobiol 1991, 120:257-266.
  • [49]Salonen K, Rosenberg M: Advantages from diel vertical migration can explain the dominance of Gonyostomum semen (Raphidophyceae) in a small, steeply-stratified lake. J Plankton Res 2005, 22:1841-1853.
  • [50]Shade A, Jones SE, McMahon KD: The influence of habitat heterogeneity on freshwater bacterial community composition and dynamics. Environ Microbiol 2008, 10:1057-1067.
  • [51]Nelson CE: Phenology of high-elevation pelagic bacteria: the roles of meteorologic variability, catchment inputs and thermal stratification in structuring communities. ISME J 2009, 3:13-30.
  • [52]Colombet J, Sime-Ngando T, Cauchie HM, Fonty G, Hoffmann L, Demeure G: Depth-related gradients of viral activity in Lake Pavin. Appl Environ Microbiol 2006, 72:4440-4445.
  • [53]Carlson RE: A trophic state index for lakes. Limnol Oceanogr 1977, 22:361-369.
  • [54]Arar EJ, Collins GB: In vitro determination of chlorophyll a and phenophytin a in marine and freshwater algae by fluorescence. U.S. Environmental Protection Agency, Method 445.0; 1997.
  • [55]Koroleff F: Determination of phosphorus. Chemistry of the element in seawater. In Methods of seawater analysis. Edited by Grasshoff K, Erhardt M, Kremling K. Weinheim: Verlag Chemie; 1983:125-139.
  • [56]Porter KG, Feig YS: The use of DAPI for identifying and counting aquatic microflora. Limnol Oceanogr 1980, 25:943-948.
  • [57]Rodriquez G, Phipps D, Ischiguro K, Ridgeway HF: Use of fluorescent redox probe for direct visualization of actively respiring bacteria. Appl Environ Microbiol 1992, 58:1801-1808.
  • [58]Zweifel UL, Hagström Å: Total counts of marine bacteria include a large fraction of non-nucleoid containing bacteria (ghosts). Appl Environ Microbiol 1995, 61:2180-2185.
  • [59]Haugland RP: Handbook of fluorescent probes and research chemicals. 2001. http://www.invitrogen.com webcite
  • [60]Chróst RJ, Overbeck J, Wcisło R: [3H] thymidine method for estimating bacterial growth rates and production in lake water: re-examination and methodological comments. Acta Microbiol Pol 1988, 37:95-112.
  • [61]Foissner W, Berger H, Schaumburg J: Identification and ecology of limnetic plankton ciliates. München: Informationberichte des Bayer Landesamtes für Wasserwirtschaft; 1999.
  文献评价指标  
  下载次数:104次 浏览次数:107次