Report on surveys of the Whitsundays sector of the Great Barrier Reef


Summary

  • Eight reefs were surveyed in the sector using fixed transects surveys.
  • Four reefs were surveyed using manta tow surveys.
  • First surveys since Severe Tropical Cyclone Debbie in 2017.
  • Sector wide coral cover was moderate.
  • No crown-of-thorns-starfish were recorded.
  • Coral bleaching was recorded at half the reefs surveyed, but at low levels (scattered, individual colonies).

Hard Coral Cover 0-10% 10-30% 30-50% 50-75% 75-100%

Figure 1: Map showing location of reefs in the Whitsundays sector.

As part of the Long-term Monitoring Program (LTMP), manta tow surveys of hard coral cover and the abundance of the coral feeding crown-of-thorns starfish (COTS), Acanthaster cf. solaris* were completed on four reefs in the Whitsundays sector of the Great Barrier Reef (GBR). Preliminary results of the manta tow surveys are presented in Tables 1 and 2.

Based on the four reefs surveyed by manta tow, the sector-wide median hard coral cover was moderate (10-30%), and has remained stable since the previous surveys in 2017. The 2017 surveys were completed just before the passage of Severe Tropical Cyclone Debbie, which passed over the Whitsundays region intensifying to a category 4 system before making landfall near Airlie Beach.

Two outer shelf reefs increased in hard coral cover from 2017 levels, indicating limited impacts from Severe Tropical Cyclone Debbie. In contrast, hard coral cover declined on two mid-shelf reefs most likely due to the passage of that cyclone. Manta tow surveys were not conducted on the inshore reefs due to poor visibility. Results from scuba surveys of coral cover on fixed sites on three inshore reef (Langford and Bird Island, Border Island and Hayman Island) indicated a decline in coral cover for these reefs due to the effects of Cyclone Debbie. This was particularly evident on Hayman Island Reef where coral cover declined from 37% to 5%. A third mid-shelf reef that was surveyed by scuba only (Hyde Reef) exhibited an increase in coral cover.

Scuba surveys at fixed transects on eight reefs recorded low levels of bleaching restricted to scattered individual colonies that was most likely the result of low cumulative heat stress over the preceding summer months. No COTS were recorded during either manta tow or fixed site surveys at any of the reefs. Counts of coral disease, include white syndrome, black band disease, brown band disease and skeletal eroding band disease were low during fixed site surveys at all reefs. Densities of the corallivorous snail Drupella spp. was low on all reefs.

Details of the manta tow method can be found in the Standard Operational Procedure No. 9 [AIMS Research - Crown-of-thorns Starfish and Coral Surveys - Standard Operational Procedure 9]. Further details of the monitoring program design, sampling methods and a full explanation of the A. solaris outbreak terminology can be found on the AIMS website.

*Note: genetic studies show that there are at least four species of COTS. These are the North and South Indian Ocean species (A. planci and A. mauritiensis), a Red Sea species (not yet named) and a Pacific species. The range of the Pacific includes the Great Barrier Reef and it has been provisionally named Acanthaster solaris (Haszprunar et. al. 2017).

 

Figure 3: Estimates for benthic data and fish abundance from fixed site surveys. Data are mean estimates ± 95% credible intervals derived from Bayesian hierarchical linear models. Total fish abundance is the combined counts of two groups of fishes that have different maximum body sizes and are surveyed differently. Large bodied fish are highly mobile, generally have maximum sizes > 15cm and are counted by a trained diver in a 5m wide swathe along each transect. Small bodied fish are all site dependent damselfishes, mostly <15cm long, that are counted along a 1m wide swathe. The trends in abundance for two specific groups of large bodied fish that are particularly important for different reasons are also shown; large herbivorous fish aid reef resilience by removing algae that may otherwise out-compete corals and harvested fish have great economic and social value.