Abstract:We used artificial substrates (rocks < 1500 cm2 surface area) in shallow water (2 m) to assess the development of epilithic macroinvertebrate communities in the presence of zebra mussels. At a turbulent site (Wheatley, Lake Erie), previously colonized (with a non-zebra mussel community) and uncolonized rocks left for 1 year both had lower densities of total invertebrates than previously colonized rocks recovered after only 1 day. As zebra mussels colonized the rocks, Gammarus sp. (amphipods) increased in densi… Show more
“…Wisenden and Bailey 1995). We found Temporal variation in zebra mussel (Dreissena polymorpha) density 2735 the density of the dominant amphipod G. roeselii was also related to the production of zebra mussel biodeposits only in LLC (Figs.…”
Section: Comparison Of the Lake Basinsmentioning
confidence: 81%
“…In comparison, the sampling site in LLC on an east shore is more wind-exposed, and therefore more turbulent, which influences the benthic community structure (Scheifhacken et al 2007). Zebra mussels can tolerate and stabilize turbulent conditions simply by the physical presence of their shells, which may facilitate settlement of other invertebrates on soft as well as on hard substrates (Dusoge 1966;Wisenden and Bailey 1995;Bially and MacIsaac 2000). The differences in the benthic community in LLC were an interactive effect of zebra mussel density (via stabilisation) and wind exposure, whereas the stabilising effect of zebra mussels was of less importance in the more sheltered sampling site in ULC.…”
“…Wisenden and Bailey 1995). We found Temporal variation in zebra mussel (Dreissena polymorpha) density 2735 the density of the dominant amphipod G. roeselii was also related to the production of zebra mussel biodeposits only in LLC (Figs.…”
Section: Comparison Of the Lake Basinsmentioning
confidence: 81%
“…In comparison, the sampling site in LLC on an east shore is more wind-exposed, and therefore more turbulent, which influences the benthic community structure (Scheifhacken et al 2007). Zebra mussels can tolerate and stabilize turbulent conditions simply by the physical presence of their shells, which may facilitate settlement of other invertebrates on soft as well as on hard substrates (Dusoge 1966;Wisenden and Bailey 1995;Bially and MacIsaac 2000). The differences in the benthic community in LLC were an interactive effect of zebra mussel density (via stabilisation) and wind exposure, whereas the stabilising effect of zebra mussels was of less importance in the more sheltered sampling site in ULC.…”
“…Experimental attempts have been made to interpret various roles provided by mussels in terms of protection from waves, provision of complex 3-dimensional habitat (Dean 1981) or creation of nutrient-rich sediments (Kautsky & Evans 1987) for marine (Suchanek 1985, Tsuchiya & Nishihira 1986) and freshwater mussels (Wisenden & Bailey 1995, Ricciardi et al 1997). In many of these studies, only some aspects of the physical and biological features of the mussels were investigated, and in only a few cases, assemblages in experimental clumps of mussels were compared to those among natural mussels (Ricciardi et al 1997).…”
Section: Resale or Republication Not Permitted Without Written Consenmentioning
“…competition for space or overgrowing snail shells by the bivalve (e.g. DUSOGE 1966, GIZIÑSKI & WOLNOMIEJSKI 1982, TUCKER 1994, WISENDEN & BAILEY 1995, HOWELL et al 1996, RICCIARDI et al 1997, GREEN-WOOD et al 2001.…”
Section: Effect Of D Polymorpha On Other Molluscs and The Whole Macrmentioning
Spatio-temporal variation in qualitative and quantitative occurrence of malacofauna was analysed in three large lowland dam reservoirs. Differences between the malacofauna of flooded land areas and former river beds persist even in middle-aged reservoirs. Quick turnover of water has a positive effect on mollusc abundance and species richness of the whole reservoir, and on the frequency of occurrence in the former river bed. Considerable dynamics of the malacocoenoses and a possibility to revert to earlier development stages, as a result of considerable disturbance, were observed at an advanced stage of biocoenosis development. Besides water dynamics and composition and distribution of bottom deposits, a significant effect on the malacocoenoses is exerted by dominant species, especially D. polymorpha. Abundance and dominance structure of malacocoenoses determine their role in the ecosystem, including accumulation of phosphorus and heavy metals, and their cycling as a result of filtration activity, faeces production, excretion and trophic transfer. Generally, the quantities of elements, especially heavy metals, accumulated in molluscs, are much smaller than the quantities which flow through the malacocoenoses. A large part of the pool of these elements contained in the shells is excluded from circulation for many years. Food chains seem to have relatively little effect on the transfer of heavy metals in the reservoir.
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