Abstract

This paper reports the alpha and beta diversity of phytoplankton communities of two streams differing in land use. We analyzed which environmental conditions affect diversity of the phytoplankton communities and tested the hypothesis that stream stretches protected by forests will have lower species richness, whereas higher beta-diversity would occur among the non-protected stretches. Samples were taken quarterly, from February to November 2012, in nine stretches, including four non-protected stretches, two partially protected stretches and three totally forest-protected stretches. Eleven abiotic variables and their coefficients of variation were analyzed. Phytoplankton was analyzed for species richness (alpha diversity), frequency of occurrence and beta-diversity. Species richness was calculated by first and second order jackknife indexes. Biotic data were submitted to Sorensen similarity analysis. A total of 429 infrageneric taxa were reported, representing 88% of the estimated expected species richness. The phytoplankton composition was typical for lotic environments with high richness values of Bacillariophyceae (66.0%). High phytoplankton richness values occurred in all the sampled stretches, even though beta-diversity was moderate and indicated similarity between the sampled stretches, therefore only a part of the original hypothesis was corroborated.

Highlights

  • Phytoplankton communities consist of photoautotrophic microorganisms (Reynolds 1984) suspended in aquatic environments that move passively due to the movements of winds and currents

  • This paper reports the alpha and beta diversity of phytoplankton communities of two streams differing in land use

  • It should be emphasized that closeness between the observed and the estimated expected species richness indicates that the sampling effort was adequate to reveal the diversity of phytoplankton in the two study rivers (Nogueira et al 2010)

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Summary

Introduction

Phytoplankton communities consist of photoautotrophic microorganisms (Reynolds 1984) suspended in aquatic environments that move passively due to the movements of winds and currents. Phytoplankton comprise a great diversity of species of a wide variety of forms and sizes, each with its own unique physiological requirements (Reynolds 2006). Information on phytoplankton communities (such as composition, structure, and spatial and temporal variability) in continental water ecosystems can elucidate the functioning of, and the energy flow within, these environments (Rodrigues 2004). Since phytoplankton communities respond rapidly to a wide variety of environmental disturbances (Cottingham & Carpenter 1998; Lepistö et al 2004; Paerl & Huisman 2009) and present a high diversity of species in natural conditions (Hutchinson 1961; 1976; Reynolds 1984; 2006), they can serve as important indicators of environmental disarray. Species diversity is a quality of biological communities that is deeply related to stability, productivity, trophic structure and migratory processes (Stirling & Wilsey 2001)

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