Methods
§ Photo quadrats at four sites (2 each of high and low human
disturbance) were taken before, just after, and three months
after the storm that occurred in late January, 2015 to quantify the effect of the storm on
benthic community assemblages (n=352).
§ The impacts of the storm were investigated using multinomial regression looking at two
aspects of benthic communities:
Overall changes in substrate The changes in percent cover of
coral, algae, and sediment were examined to look at the overall changes in substrate
composition at each site.
Changes in dominant coral morphologies
The impacts of the storm on five coral morphologies were
examined to determine changes in structural complexity of reef ecosystems and dominant coral morphologies.
Acknowledgments
We thank our collaborators and field assistants: K. Tietjen, J. McDevitt-Irwin, J. Burns, K. Cox. We gratefully acknowledge the support NSERC, JCURA, Rufford Smalll Grants for Nature, and NSF provide for our research goals. Images used by permission of the Baum lab.
Background
Results
Changes in substrate types:
Figure 1. Changes in the occurrences of substrate types at two sites of low human disturbance (Low1 and Low2) and two sites of high human disturbance (High1 and High2) with 95% credible intervals. A shows the changes in the probability of occurrence of each substrate type across three sample
times: before- August 2014, After 1-February 2015 (immediately after the storm) and After 2-May 2015 (3 months after the storm). B shows the changes in substrate composition between the Before and After1 sampling times; a negative value indicates a decline in the proportion of that substrate. The group “other” includes invertebrates other than coral, hard substrates and sand.
Storm waves on Kiritimati in January 2015; storm damage at a site of low human disturbance;
Montipora sp. covered in sediment after the storm
Changes in coral morphologies:
Figure 2. Changes in the occurrences of five coral morphologies at two sites of low human
disturbance (Low1 and Low2) and two sites of high human disturbance (High1 and High2) with 95% credible intervals. A shows the probability of occurrence of each morphology across three
sample times: before- August 2014, After 1-February 2015 (immediately after the storm) and After 2-May 2015 (3 months after the storm). B shows the changes in morphology composition between the Before and After1 sampling times; a negative value indicates a decline in the proportion of that
morphology.
Results
Changes in substrate types:
Changes in dominant coral morphologies:
Lisa Szostek, Geoffrey J. Osgood, Danielle C. Claar, Julia K. Baum
Department of Biology, University of Victoria
PO Box 1700 STN CSC
Victoria, BC, V8W 2Y2, Canada
Literature Cited
1. Pandolfi, J.M., Bradbury, R.H., Sala, E., Hughes, T.P., Bjorndal, K.A., Cooke, R. G., McArdle, D., McClenachan, L., Newman, M.J.H., Paredes, G., Warner, R.R., & Jackson,
J.B.C. (2003). Global trajectories of the long-term decline of coral reef ecosystems. Science, 301,
955-958.
2. Fribourg, A.S. (1999). Global change and the decline of coral reefs. Swiss Journal of Geography,
54, 125-131.
3. Emanuel, K. (2005). Increasing destructiveness
of tropical cyclones over the past 30 years.
Nature, 436, 686-688.
4. Webster, P.J., Holland, G.J., & Curry, J.A.
(2005) Change, H.R. Changes in tropical cyclone number, duration and intensity in a warming environment. Science, 309, 1844-1846.
5. Norstrom, A.V., Nystrom, M., Lokrantz, J., & Folke, C. 2009. Alternative states on coral reefs: beyond coral-macroalgal phase shifts. Marine
Ecology Progress Series. 376, 295-306.
6.. Alvarez-Filip, L., Dulvy, N.K., Gill, J.A., Cote, I.M., & Watkinson, A.R. 2009. Flattening of
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Further Information
§ Contact information:
Email: lszostek@uvic.ca
§ We invite you to learn more about: research in the Baum Lab
baumlab.weebly.com
Next Steps
§ Incorporating more sites of both high and low human disturbance into this study
§ Continued monitoring of the reef ecosystem to assess
recovery, as well as the impacts of other threats such as ENSO events.
§ Coral reef communities are in
decline as a result of anthropogenic
and natural threats including storm
events, which are hypothesized to
increase in intensity and frequency
due to climate change
1,2,3,4.
§ Disturbances have a tendency to
shift benthic communities to a
macro-algae dominated state and
to shift coral species from
structurally complex reef building
species to less complex species
5,6.
§ These changes lead to a decreased
ability to support reef fishes which
thousands of people rely on
worldwide for subsistence
5,6.
§ This study quantified the impacts
that a severe storm had on benthic
community structure on Kiritimati,
Kiribati.
B
A
A
B
§ Our results indicate that coral cover and algae cover declined after the storm to favour a sediment
dominated state (Figure 1).
§ These results were consistent across sites of high and low human
disturbance and no significant difference in the magnitude of
changes between sites of different disturbance levels was observed. § An insignificant difference in
changes in substrates between the two post-storm sampling times
indicate that the storm was the driver of the changes in benthic
substrates and that recovery did not occur within three months of the
storm event (Figure 1A).