pink coral image with fish

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

Summary

 

  • Overall, sector-wide coral cover has increased
  • Reefs in this sector continue to recover from the combined effects of cyclones and COTS
  • COTS remain active on reefs in this sector

 

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

Figure 1: Map showing location of reefs in the Pompeys sector. Click the points for more information.

 

Table 1: Overview of results obtained from manta tow surveys of reefs in the Pompeys sector

 

Pompeys Sector Summary Trend since last survey
Average Coral Cover (%) 24.9 Increased
COTS status: 1 Active Outbreaks, 1 Incipient Outbreaks Increased
Coral bleaching: None Stable

 

 

As part of the Long Term Monitoring Program (LTMP), manta tow surveys of coral cover and abundance of the coral feeding crown-of-thorns starfish (COTS), Acanthaster cf. solaris* were completed on eleven reefs in the Pompey sector of the Great Barrier Reef. Results of the manta tow surveys are presented in Tables 1 and 2. Overall, the average sector-wide live coral cover had increased (Table 1). Coral cover increased significantly on three reefs since last surveyed (Reef 20-353, Reef 21-139 and Pompey Reef #1) while a further five reefs showed a trend of increasing coral cover (Reef 21-060, Reef 21-187, Pompey Reef #2, Ben Reef and Tern Reef). Increases in live coral cover have occurred on reefs as they recover from impacts experienced over the last decade. These have been mainly due to cyclones (i.e. Severe Cyclone Hamish, March 2009, Cyclone Ita in April 2014, Severe Cyclone Marcia in February 2015 and Severe Cyclone Debbie in 2017) and COTS. For those reefs where coral cover had decreased since last surveyed, Reef 21-591 and Penrith Island Reef, declines were likely due to Cyclone Marcia and Cyclone Ita respectively. The latest surveys showed COTS activity had increased (Table 1) on reefs in this sector with two reefs, Reef 21-064 and Reef 21-187 at outbreak levels and low-level COTS activity observed on a third, Reef 21-139. Coral cover remained low on Reef 21-064 due to ongoing COTS activity but had increased on Reef 21-187 and Reef 21-139 despite the presence of COTS.

Scuba surveys of agents of coral mortality were conducted along fixed transects on all reefs except for Ben Reef. Low levels of coral bleaching, restricted to a few scattered individual coral colonies, were recorded on Reef 21-591, Penrith Island Reef, Pompey Reef #2 and Tern Island Reef. There were some cases of white syndrome coral disease on the majority of reefs and incidences were generally at the lower end of the historical range. This also the case for three other coral diseases (black-band, brown-band, and skeletal eroding band disease) that were generally absent, but where present affected only a few individual colonies. The corallivorous snail, Drupella spp. were present at most reefs and were generally at the lower end of the range of abundances recorded in previous years except for Reef 20-353 where numbers were slightly elevated.

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. c.f. 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).

 

Table 2: Summary of manta tow surveys of reefs in the Pompeys sector. Arrows indicate the trend in live coral cover and A. solaris since last survey; ▲ = increase, ▼ = decrease, " " = no change. Outbreak Status: NO no outbreak, PO potential outbreak >0.1 COTS per tow, IO incipient outbreak >.22 COTS per tow, RE recovering, AO = Active Outbreak>1 COTS per tow.

Reef Shelf Position Tows Previous survey year Total A. solaris per reef A. solaris per tow A. Solaris Outbreak Status Live Hard Coral Cover % Soft Coral Cover % Survey Year
20353S Mid 25 2018 0 0 NO 45.7 ▲ 2.4 ▲ 2020
21060S Mid 21 2018 0 0 RE 10.2 ▲ 2.5 2020
21064S Mid 24 2018 45 1.88 ▲ AO ▲ 6.7 ▲ 2.9 ▲ 2020
21139S Mid 60 2018 1 0.02 ▲ NO 57.1 ▲ 2.7 ▲ 2020
21187S Mid 42 2018 27 0.64 ▲ IO ▲ 40.4 ▲ 2.3 ▲ 2020
21591S Mid 26 2014 0 0 NO 16 ▼ 7.1 ▼ 2020
POMPEY REEF (NO 1) Mid 50 2018 0 0 NO 32 ▲ 3.3 ▼ 2020
POMPEY REEF (NO 2) Mid 36 2018 0 0 NO 10.2 ▲ 4.9 ▼ 2020
TERN REEF(20309) Mid 28 2018 0 0 ▼ RE 27 ▲ 3.1 ▼ 2020
BEN REEF Outer 12 2017 0 0 NO 41.7 ▲ 2.3 ▼ 2020
PENRITH REEF Mid 56 2010 0 0 NO 17.1 ▼ 7 ▼ 2020

Figure 2: - Sector-wide changes in coral cover and the numbers of A. solaris for survey reefs in the Pompeys sector of the GBR. Orange trend line = Hard coral. Purple bars = Crown-of-thorns (COTS)

Figure 2: - Sector-wide changes in coral cover and the numbers of A. solaris for survey reefs in the Pompeys sector of the GBR. Orange trend line = Hard coral. Purple bars = Crown-of-thorns (COTS)

Image 1. Crown-of-thorns starfish (COTS) remain active on reefs in this sector. Reef 21-064 is currently experiencing an Active Outbreak. Image 1. Crown-of-thorns starfish (COTS) remain active on reefs in this sector. Reef 21-064 is currently experiencing an Active Outbreak.
Image 2. Cyclones in recent years have had a big impact on many reefs in this sector. This rubble bank on Penrith Island is covered in golden noodle algae; an invasive species that is likely to impede coral settlement. Image 2. Cyclones in recent years have had a big impact on many reefs in this sector. This rubble bank on Penrith Island is covered in golden noodle algae; an invasive species that is likely to impede coral settlement.
Image 3. While some reefs are slow to recover others do so more quickly. This photograph was taken on Ben Reef where coral cover is has increased considerably since it was devastated by Cyclone Hamish in 2009. Image 3. While some reefs are slow to recover others do so more quickly. This photograph was taken on Ben Reef where coral cover is has increased considerably since it was devastated by Cyclone Hamish in 2009.