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Toxic M icrocystis (cyanobacteria) inhibit recruitment of the bloom‐enhancing invasive bivalve L imnoperna fortunei
Author(s) -
Boltovskoy Demetrio,
Correa Nancy,
Bordet Facundo,
Leites Valentín,
Cataldo Daniel
Publication year - 2013
Publication title -
freshwater biology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.297
H-Index - 156
eISSN - 1365-2427
pISSN - 0046-5070
DOI - 10.1111/fwb.12184
Subject(s) - mussel , cyanobacteria , biology , bloom , algae , algal bloom , zooplankton , larva , water column , ecology , biomass (ecology) , reproduction , microcystin , phytoplankton , nutrient , genetics , bacteria
Summary Toxic cyanobacterial blooms and biological invasions are major threats to freshwater systems worldwide. While usually dealt with independently, the two threats can interact to produce synergistic or antagonistic outcomes. The aim of this survey is to analyse interactions between the cyanobacterium M icrocystis spp. and the A sian invasive mussel L imnoperna fortunei . On the basis of 9 years of observational data in a large subtropical reservoir ( S alto G rande, A rgentina– U ruguay), we analyse causal relationships between recurring summer–early autumn blooms of M icrocystis spp. and recruitment by L . fortunei . Reproduction of the mussel was interrupted during dry summers ( J anuary– A pril), coinciding with periods of peak M icrocystis spp. growth and low water discharge (which favours build‐up of algal biomass). On the other hand, wet summers with high discharge rates were characterised by low M icrocystis spp. densities and high numbers of L . fortunei larvae in the water column. Of the seven S outh A merican waterbodies investigated, S alto G rande was the only one with very marked cyanobacterial blooms and where larval numbers decrease to near zero during J anuary– A pril; in all others, reproduction peaks in J anuary– A pril. The assumption that microcystin‐producing algae are responsible for these troughs during periods when elsewhere larvae are very abundant was reinforced by experimental results indicating that microcystin‐ LR is highly toxic to the mussel's larvae, eliminating 58–100% of animals in 48 h at 10–20 μg L −1 . Paradoxically, high concentrations of microcystin in water are probably partly due to L . fortunei 's own activity, which enhances growth of M icrocystis spp. through modification of nutrient concentrations, selective grazing of solitary M icrocystis spp. cells over colonial ones and production of chemical cues that trigger the formation of colonies. These interactions have important implications for the management of biofouling of industrial raw cooling water facilities by the byssate mussels, as well as policies oriented at curtailing the spread of the invasive bivalve.