2018 ESA Annual Meeting (August 5 -- 10)

PS 49-10 - Beyond eutrophication: Vancouver Lake, WA, as a model system for assessing multiple, interacting biotic and abiotic drivers of harmful cyanobacterial blooms

Friday, August 10, 2018
ESA Exhibit Hall, New Orleans Ernest N. Morial Convention Center
Gretchen Rollwagen-Bollens1,2, Tammy Lee3, Vanessa Rose3 and Stephen M. Bollens1,3, (1)School of Biological Sciences, Washington State University, Vancouver, WA, (2)School of the Environment, Washington State University, WA, (3)School of the Environment, Washington State University, Vancouver, WA
Background/Question/Methods

Eutrophication of lakes and reservoirs has contributed to an increase in the magnitude and frequency of harmful cyanobacterial blooms; however, the interactive effects of nutrient availability (eutrophication) and other abiotic and biotic drivers have rarely been comprehensively studied in the field. We undertook a unique 8-year (2005-2013) research program that assessed the interaction of multiple factors driving cyanobacterial blooms in Vancouver Lake, a large, shallow eutrophic lake in Washington, USA. Our program consisted of nearly continuous monthly or weekly monitoring of water quality and plankton community composition over eight years, as well as multiple zooplankton grazing experiments over three years.

Results/Conclusions

We observed a relatively consistent seasonal succession of phytoplankton and zooplankton assemblages, and a pattern of interacting factors influencing cyanobacterial bloom dynamics. In the 2-3 weeks before a bloom, a combined effect of decreased dissolved nitrogen (N), a sudden increase of dissolved phosphorus (P), and a cascading effect of zooplankton grazing created a ‘perfect storm’ of conditions that promoted the rapid proliferation of cyanobacteria. At the blooms’ peaks, cyanobacterial carbon biomass reached as high as 20 µg L-1, with total [chl a] often exceeding 750 µg L-1. In the weeks following the blooms’ peaks, [PO4-P] and [NH4-N] dropped and copepod feeding rates fell to near zero, whereas microzooplankton grazing rates reached their maxima. Microzooplankton grazing impact, combined with low nutrient availability, then drove down cyanobacteria abundance. Vancouver Lake serves as a model for understanding multiple, interacting drivers of cyanobacterial bloom dynamics in shallow, temperate lakes, and is therefore an important system in which to investigate new questions related to the science and management of harmful cyanobacterial blooms.