Heat-Induced Stress in Corals is Exacerbated by Eutrophication
Fabricius, K.E., Cseke, S., Humphrey, C. and De'ath, G. 2013. Does trophic status enhance or reduce the thermal tolerance of scleractinian corals? A review, experiment and conceptual framework. PLOS ONE 8: e54399.
To help resolve this issue, Fabricius et al. conducted a 90-day-long experiment in which they maintained colonies of two scleractinian corals (Acropora millepora and Montipora tuberculosa) in either (1) normal coastal seawater or (2) normal coastal seawater that was further "organically and nutrient enriched (OE)," both with and without heat stress, where in the former case water temperature was gradually increased from 27 to 31.2°C for another 3-7 weeks.
After the 3-7 weeks of heat stress, the four researchers report that colonies of both species had significantly greater reductions in fluorescence yields and lower survival in the OE treatment than in the non-OE-treated coastal water. In addition, they say that photophysiological recovery was incomplete 31-38 days after ending the heat stress only in the OE treatment.
Fabricius et al. conclude that their study "adds to mounting evidence that eutrophication can worsen thermal stress on inshore reef communities," and that "even without heat stress, the exposure to organical enrichment has strong negative effects on the photophysiology and survival of inshore corals (Fabricius et al., 2003; Weber et al., 2006; Weber et al., 2012)." And they say that "improving water quality, by reducing the loss of fertilizers and soils from farmed and cleared lands, is therefore rightly considered an essential management strategy to enhance the resilience of reefs to warming temperatures and ocean acidification," citing Wooldridge et al. (2006), the State of Queensland and Commonwealth of Australia (2009), and the Secretariat of the Convention on Biological Diversity (2010).
Fabricius, K.E., Wild, C., Wolanski, E. and Abele, D. 2003. Effects of transparent exopolymer particles and muddy terrigenous sediments on the survival of hard coral recruits. Estuarine and Coastal Shelf Science 57: 613-621.
Secretariat of the Convention on Biological Diversity. 2010. COP 10 Decision X/2. Strategic Plan for Biodiversity 2011-2020 and the Aichi Targets. Secretariat of the Convention on Biologicl Diversity, Montreal, Canada.
The State of Queensland and Commonwealth of Australia. 2009. Reef Water Quality Protection Plan for Catchments Adjacent to the Great Barrier Reef World Heritage Area. Queensland Department of premier and Cabinet, Brisbane, Australia.
Weber, M. de Beer, D., Lott, C., Polerecky, I. Kohls, K., Abed, R.M. M, Ferdelman, T.G. and Fabricius, K..E. 2012. Mechanisms of damage to corals exposed to sedimentation. Proceedings of the National Academy of Sciences USA 109: E1558-67.
Weber, M., Lott, C. and Fabricius, K. 2006. Different levels of sedimentation stress in a scleractinian coral exposed to terrestrial and marine sediments with contrasting physical, geochemical and organic properties. Journal of Experimental Marine Biology and Ecology 336: 18-32.
Wooldridge, S., Brodie, J. and Furnas, M. 2006. Exposure of inner-shelf reefs to nutrient enriched runoff entering the Great Barrier Reef Lagoon: Post-European changes and the design of water quality targets. Marine Pollution Bulletin 52: 1467-1479.