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Bridging GLEON sites with Gloeotrichia echinulata

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Title: Bridging GLEON sites with Gloeotrichia echinulata


1
Bridging GLEON sites with Gloeotrichia echinulata
  • Cayelan Carey1
  • Kathleen Weathers2
  • Kathryn Cottingham3
  • Irene Karlsson-Elfgren1

1Uppsala University, Sweden 2Institute of
Ecosystem Studies, USA 3Dartmouth College, USA
2
Gloeotrichia echinulata
  • Toxic N-fixing cyanobacterium
  • Discrete benthic and planktonic life stages
  • Impact of blooms on a lake ecosystem

(1-2 mm)
(Istvanovics et al. 1993, Pettersson et al. 1993,
Jacobsen 1994, Forsell and Pettersson 1995,
Pettersson 1998, Hyenstrand et al. 2001,
Karlsson 2003, Karlsson-Elfgren et al. 2003,
Karlsson-Elfgren et al. 2005)
3
Lake Erken, Sweden
  • Long history of G. echinulata blooms in Lake
    Erken
  • Documented relationships between light,
    temperature, stratification and G. echinulata
    recruitment

Lake Erken
Pierson et al. 1992, Forsell and Pettersson 1995,
Hyenstrand et al. 2001, Karlsson 2003,
Karlsson-Elfgren et al. 2003, Karlsson-Elfgren et
al. 2004, Karlsson-Elfgren et al. 2005
4
Lake Sunapee, USA
  • Recent G. echinulata outbreaks across the
    northeastern United States
  • gt 27 oligotrophic lakes have exhibited blooms
    since 2002

5
My questions
  • What factors are causing G. echinulata to bloom
    in oligotrophic lakes? Do these mechanisms
    operate in eutrophic systems? Invasion or
    re-emergence?
  • How do G. echinulata blooms impact an
    oligotrophic lake ecosystem?
  • Lake phosphorus cycling, toxicity, phytoplankton
    and zooplankton community structure, and trophic
    status

6
The role of sediment P in triggering G. echinulata
  • G. echinulata is dependent primarily on P in the
    sediments, not water column
  • Used field monitoring, lab experiments, and an in
    situ nutrient-diffusing experiment to examine the
    role of TP at the sediment-water interface on
    recruitment

7
Lake monitoring results
2005 2006
G. echinulata recruitment rate is correlated with
pore water TP, lagged by 25 days (r 0.53).
8
2005 Sediment TP and G. echinulata pulses
9
2005 Sediment TP and G. echinulata pulses
Germination (1 week)
Phosphorus Absorption (2.5 weeks)
10
Nutrient-diffusing experiment
P-diffusing tile
11
Nutrient-diffusing experiment
Experimental P addition significantly increased
the rate of G. recruitment 22 days after the
start of the experiment (Matched pairs t-test,
one-sided P 0.0097).
12
G. echinulata and eutrophication
Increased watershed development
G. echinulata increases lake eutrophication
processes
13
Future Erken/Sunapee GLEON research
  • Use routine monitoring data at both sites to
    evaluate other factors triggering G. echinulata
    recruitment (i.e. light, temperature, etc.)
  • Can P pulses trigger G. echinulata blooms in
    Erken?
  • Examine long-term database at Erken
  • Toxicity analyses
  • Comparing Swedish/U.S. G. echinulata phylogeny

14
Acknowledgments
  • U.S. Swedish Fulbright Commission
  • Lake Sunapee Protective Association
  • Northeast Aquatic Plant Management Society
  • Jim Haney, Center for Freshwater Biology,
    University of New Hampshire
  • Andrew W. Mellon Foundation
  • National Science Foundation

15
Questions?
Photo Karen Moore
16
G. echinulata toxicity
  • First toxicity study conducted on G. echinulata
    in Lake Sunapee produces 0.10 0.01 µg MC-LR
    g-1 dry wt. colonies
  • At peak bloom conditions in Sunapee, MC-LR
    toxicity was 6 orders of magnitude below the WHO
    guideline
  • In Lake Erken, however up to 5000 colonies L-1
    in 2004 (Eiler et al. 2006), toxicity may be
    within 2 orders of magnitude of water safety
    guideline
  • Other toxicity effects
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