Abstracts:

Dominance of Cylindrospermopsis raciborskii in Queensland tropical and subtropical reservoirs: Implications for monitoring and management

Glenn McGregor1 & Larelle Fabbro2

1Queensland Department of Natural Resources, 1345 Ipswich Road, Rocklea Qld 4016. 2Freshwater Ecology Group, Centre for Land and Water Resource Management, Central Queensland University, Rockhampton. Qld 4703


Since October 1997, 47 reservoirs and weir pools across tropical and sub-tropical Queensland have been regularly monitored for the occurrence of cyanobacteria. Cylindrospermopsis raciborskii (Woloszynska) Seenayya and Subba Raju was found in 70% of the storages, with one storage displaying year-round dominance, 50% of the reservoirs seasonally dominated, and a seasonal presence in 46% of the weir pools. Maxima for the majority of storages occurred from late summer through to early autumn. The precise timing of onset of seasonal maxima varied considerably between storages and regions. Temperature and stratification patterns influenced seasonal recruitment with C. raciborskii reaching seasonal maxima in southern storages generally later than the northern storages. Overall peak seasonal abundance occurred in deep strongly stratified storages.

The majority of storages experiencing concentrations > 15 000 cells mL-1 tested positive to the presence of the alkaloid cytotoxin,cylindrospermopsin. Median cylindrospermopsin concentration across the fourteen reservoirs in which toxin was recorded was 3.4 µg L-1. The highest toxin concentrations were generally associated with storages in which C.raciborskii had been established for a considerable period of time, or occurred after the peak summer population maxima. Toxin concentrations of 1 µg L-1 were generally associated with cell concentrations of ca. 20 000 cells mL-1, hence this cell concentration threshold was adopted as a health trigger level at which to begin monitoring for toxicity.

The morphology of this species was highly variable and included straight, coiled, and sigmoid-shaped trichomes. Populations were routinely recorded as mixtures of all three morphotypes or proceeded as transitions from one morphotype to another throughout the year. The dominance of C. raciborskii appears to be favored by a set of environmental and hydrological factors including long water residence time, high pH, high temperature, high incident irradiation and a thermally stratified water column.

The lack of visual monitoring cues such as scum formation, variation in colour of the water body, rapid germination of large numbers of cells, highly variable morphology, relative toxicity and persistence of this species year round in many areas continues to make this species a primary focus of water managers in this state.

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