Abstract
The relationships between the species richness, diversity and equitability of phytoplankton is discussed in the context of Connell’s (1978, Science 199: 1304–1310) Intermediate Disturbance Hypothesis (IDH). The records of 759 vertical phytoplankton samples, which were obtained from four shallow central European lakes (Balaton, Neusiedlersee, and two small artificial ponds) at daily to weekly intervals were analysed.
-
1)
The Shannon-Weaver function was used to measure diversity of the recorded species composition of the phytoplankton. It is shown on fictitious data that compositional diversity is sensitive to the number of coequilibrating species provided that the suspected interrelationship between diversity and ‘complexity’ is amenable to the application of this method.
-
2)
The disturbance scale that was developed on the basis of the field records fits well to Reynolds’ (1988, Verh. int. Ver. Limnol. 23: 683–691) derivation: < 3 days qualifies as high frequency, approximately 3–8 days as intermediate frequency and > 8–9 days as low frequency of disturbance for phytoplankton.
-
3)
Arithmetical means of the compositional diversity of phytoplankton under different frequencies of disturbance support the hypothesis that maximal diversity appears at intermediate frequencies.
-
4)
There are different reasons for decrease in diversity at higher and lower frequencies. Inequitability diminishes diversity at low disturbance; while species number decreases at high frequencies.
-
5)
The case of Neusiedlersee calls attention to the fact that it is difficult, if at all possible, to differentiate between the indices under continuous stress and high frequency of disturbance in lakes in temperate regions. Similar species number-equitability pattern are induced by both and it is also presumable that high frequency disturbance can itself effect a serious stress.
-
6)
The striking effects that regular major periodic events (e.g. significant changes in the grazing pressure at the onset of the clear-water phase, autumnal cooling) in the plankton have on its species diversity are evident. Thus, the relative importance of intermediate frequency disturbances has its own seasonality: it is increasingly important in periods (partly in the spring, but mostly in the summer-autumn equilibrium phases), in which competition among phytoplankton species is increasing. This observation suggests a way by which the stochasticity-based IDH can be incorporated into rather more deterministic explanations (e.g. PEG-model; Sommer et al., 1986. Archiv für Hydrobiologie 106: 433–471) of plankton succession.
-
7)
The most controversial issue and, therefore, the main difficulty, with IDH is that it not only maintains species richness in an ecosystem but it also supposes its presence. The lack of either early or late successional species in a given community can inactivate the mechanism. From the point of view of the diversity-species richness relationship, the persistence of disturbance at given frequencies is of greater importance than the temporal alterations themselves in the evolutionary ecology of the phytoplankton.
-
8)
For characteristically unperturbed phytoplankton communities (no case was studied here), equilibrium concepts (niche diversification, etc.) should be more strongly applicable to their diversity and species richness.
Access this chapter
Tax calculation will be finalised at checkout
Purchases are for personal use only
Preview
Unable to display preview. Download preview PDF.
References
Bonder, E., Gy. Dévai, I. Dévai, L. G.-T6th, Cs. Heim, A. Kovacs, J. Moldovân, J. Padisâk and I. Wittner, 1981. A case-study on some hydrobiological interactions in a sewage treatment plant. Acta Biologica Debrecina Suppl. 18: 1–292.
Chorus, I. and G. Schlag, 1993. Importance of intermediate disturbances for the species composition and diversity of phytoplankton in two very different Berlin lakes. Hydrobiologia 249: 67–92.
Connell, J., 1978. Diversity in tropical rain forests and coral reefs. Science 199: 1304–1310.
Dévai, I., 1977. Eutrophication and oligotrophication as exampled by BMKO, a sewage treatment plant. Acta biologica Debrecina 14: 67–78.
Dévai, I. and E. Woynarovich, 1981. Eutrophication and oligotrophication process occurring in a BMKO sewage treatment plant. In: M. Sudzuki (ed), Some Approaches to Saprobiological Problems. Sanseido Co. Ltd, Tokyo: 3747.
Dokulil, M. and J. Padisâk, 1993. Langzeitveränderungen der Zusammensetzung und der Populationsdynamik des Phytoplanktons im Neusiedlersee (1958, 1968–1990). — BFB Bericht.
Egler, F. E., 1954. Vegetation science concepts. I. Initial floristic composition - a factor in old-field vegetation development. Vegetatio 4: 412–417.
Gaedeke, A. and U. Sommer, 1986. The influence of the frequency of periodic disturbances on the maintenance of phytoplankton diversity. Oecologia 71: 98–102.
Gause, G. F., 1934. The struggle for existence. Williams-Wilkins, Baltimore.
Gleason, H. A., 1926. The individualistic concept of the plant association. Torrey Bot. Club Bull. 53: 7–26.
G.-Toth, L., 1980. Short term investigations on the bacterioplankton of Lake Balaton at Tihany. Acta Bot. acad. Sci. Hung. 26: 425–435.
G.-Toth, L. and J. Padisâk, 1986. Meteorological factors affecting the bloom of Anabaenopsis raciborskii Wolosz. (Cyanophyta: Hormogonales) in the shallow Lake Balaton, Hungary. J. Plankton Res. 8: 353–363.
Hardin, G., 1960. The competitive exclusion theory. Science 131: 1292–1297.
Herodek, S., 1984. The eutrophication of Lake Balaton: Measurements, modelling and management. Verh. int. Ver. Limnol. 22: 1087–1091.
Herzig, A., 1990. Zur limnologischen Entwicklung des Neusiedler Sees. AGN, Internat. Symp. Schutz und Entwicklung großer mitteleuropäischer Binnenseenlandschaften, Bodensee - Neusiedlersee - Balaton, Tagungsband: 9197.
Holloway, J. T., 1948. Ecological investigations in the Nothofagus forests in N. Z. N. Zeal. J. Forestry 5: 401410.
Holloway, J. T., 1954. Forests and climates in the South Island of New Zealand. Trans. Royal Soc. New Zeal. 82: 329–410.
Hutchinson, G. E., 1961. The paradox of plankton. Am. Nat. 95: 137–147.
Istvânovics, V. and S. Herodek, 1985. Orthophosphate uptake of planktonic microorganisms in Lake Balaton. Hydrobiologia 122: 159–166.
Istvânovics, V., L. Vörös, S. Herodek, S., L. G.-Toth and I. Tâtrai, 1986. Changes of phosphorus and nitrogen limitation in enriched lake enclosures. Limnol. Oceanogr. 31: 798–811.
Khinchin, A. I., 1957. Mathematical Foundations of Information Theory. Dover, New York.
Kullbach, S., 1957. Information Theory and Statistics. Wiley, New York.
Kiss, K. T. and J. Padisâk, 1990: Species succession of Thalassiosiraceae: Quantitative studies in a large, shallow lake (Lake Balaton, Hungary). In H. Simola (ed), Proceedings of the 10th Internat. Symp. on Living and Fossil Diatoms. Koeltz Scientific Books, Koenigstein: 481–490.
Lund, J. W. G., C. Kipling and E. D. Le Cren, 1958. The inverted microscope method of estimating algal numbers by counting and the statistical basis of enumeration by counting. Hydrobiologia 11: 143–170.
Padisâk, J., 1980. Short-term studies on the phytoplankton of Lake Balaton in the summers of 1976, 1977 and 1978. Acta Bot. Hung. 26: 397–416.
Padisâk J., 1991. Relative frequency, seasonal pattern and possible role of species rare in the phytoplankton (Lake Balaton, Hungary). Verh. int. Ver. Limnol. 24: 989–992.
Padisâk, J., 1992. Seasonal succession of phytoplankton in a large shallow lake ( Balaton, Hungary) - a dynamic approach to ecological memory, its possible role and mechanisms. J. Ecol. 80: 217–230.
Padisâk, J. and L. G.-Toth, 1991. Some aspects of the ecology of the subdominant green algae in a large nutrient limited shallow lake ( Balaton, Hungary). Arch. Protistenkunde 139: 225–242.
Padisâk, J., L. G.-Toth and M. Rajczy, 1988. The role of storms in the summer succession of phytoplankton in a shallow lake ( Lake Balaton, Hungary). J. Plankton Res. 10: 249265.
Padisâk, J., L. G.-Toth and M. Rajczy, 1990. Stir-up effect of wind on a more-or-less stratified shallow lake phytoplankton community, Lake Balaton, Hungary. In P. Biro and J. F. Taping (eds), Trophic Relationships in Inland Waters. Developments in Hydrobiology 53. Kluwer Academic Publishers, Dordrecht: 249–254. Reprinted from Hydrobiologia 191.
Pielou, E. C., 1975. Ecological diversity. Wiley and Sons Inc., New York.
Podani, J., 1988. SYN-TAX III. Computer programs for data analysis in ecology and systematics. Abstr. Bot. 12: 1–183.
Rajczy M. and J. Padisâk, 1983. DIVDROP analysis - a new method for the interpretation of species importance in diversity changes. - Ann. Hist.-nat. Mus. Nat. Hung. 75: 97–105.
Reynolds, C. S., 1988. The concept of biological succession applied to seasonal periodicity of phytoplankton. Verh. int. Ver. Limnol. 23: 683–691.
Reynolds, C. S., 1993. Scales of disturbance and their role in plankton ecology. In J. Padisâk, C. S. Reynolds and U. Sommer (eds), Intermediate Disturbance Hypothesis in Phytoplankton Ecology. Developments in Hydrobiology 81. Kluwer Academic Publishers, Dordrecht: 157–171. Reprinted from Hydrobiologia 249.
Shannon, C. E., 1948. A mathematical theory of communication. Bell Syst. tech. J. 27: 623–656.
Sommer, U., 1983. Nutrient competition between phytoplankton species in multispecies chemostat experiments. Archiv für Hydrobiologie 96: 399–416.
Sommer, U., 1984. The paradox of plankton: fluctuations of phosphorus availability maintain diversity in flow-through cultures. Limnol. Oceanogr. 29: 633–636.
Sommer, U., 1985. Comparisons between steady state and non-steady state competitions: experiments with natural phytoplankton. Limnol. Oceanogr. 30: 335–346.
Sommer, U., 1991. Phytoplankton: directional succession and forced cycles. In H. Remmert (ed), The Mosaic-Cycle Concept of Ecosystems. Springer Verlag, Berlin: 132–146.
Sommer, U., Z. M. Gliwicz, W. Lampert and A. Duncan, 1986. The PEG-model of seasonal succession of planktonic events in freshwaters. Archiv für Hydrobiologie 106: 433–471.
Sommer, U., J. Padisâk, C. S. Reynolds and P. Juhâsz-Nagy, 1993. Hutchinson’s heritage: the diversity-disturbance relationship in phytoplankton. In J. Padisâk, C. S. Reynolds and U. Sommer (eds), Intermediate Disturbance Hypothesis in Phytoplankton Ecology. Developments in Hydrobiology 81. Kluwer Academic Publishers, Dordrecht: 1–7. Reprinted from Hydrobiologia 249.
Sorensen, T., 1948. A method for establishing groups of equal amplitude in plant sociology based on similarity of species content and its application to analyses of the vegetation on Danish commons. Biol. Skr. 5: 1–34.
Tilman, D., 1982. Resource competition and community structure. Princeton Univ. Press.
Trimbee, A. M. and G. P. Harris, 1983. Use of time series analysis to demonstrate advection rates of different variables in a small lake. J. Plankton Res. 5: 819–833.
Vörös, L. and J. Padisâk, 1991. Phytoplankton biomass and chlorophyll-a in some shallow lakes in central Europe. Hydrobiologia 215: 111–119.
Wilson, J. B., 1990. Mechanisms of species coexistence: twelve explanations for Hutchinson’s `paradox of the plankton’: evidence from New Zealand plant communities. New Zeal. J. Ecol. 13: 17–42.
Author information
Authors and Affiliations
Editor information
Rights and permissions
Copyright information
© 1993 Springer Science+Business Media Dordrecht
About this paper
Cite this paper
Padisák, J. (1993). The influence of different disturbance frequencies on the species richness, diversity and equitability of phytoplankton in shallow lakes. In: Padisák, J., Reynolds, C.S., Sommer, U. (eds) Intermediate Disturbance Hypothesis in Phytoplankton Ecology. Developments in Hydrobiology, vol 81. Springer, Dordrecht. https://doi.org/10.1007/978-94-017-1919-3_14
Download citation
DOI: https://doi.org/10.1007/978-94-017-1919-3_14
Publisher Name: Springer, Dordrecht
Print ISBN: 978-90-481-4233-0
Online ISBN: 978-94-017-1919-3
eBook Packages: Springer Book Archive