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We survey transects (paths) across each of the two island communities in the Abbot Point region, both pre- and post-wet season. At each transect, benthic (seafloor) cover is classified into categories of cover type and provides information on the dominant reef structure (hard or soft), as well as the extent of macroalgae, which can impede the growth of corals. Information on the extent of bleached, diseased or damaged corals is also determined, which provides information on the health of the coral community. Click below on each site.
Camp Island is dominated by macroalgae with levels consistently above 30%. Hard coral cover, while largely unaffected by TC Debbie, was severely impacted by a mass bleaching event in 2020 decreasing hard coral by 54% from October 2019 to June 2021. The bleaching event (2020) reduced macroalgae and led to a significant loss of hard corals (2019 to 2021). Hard coral cover has started to significantly increase as of May 2022 since the 2020 bleaching event.
The major regional scale bleaching event in early 2020 led to significant bleaching of Holbourne Island hard corals communities but to a lesser extent than at Camp Island; likely in part due to the slightly deeper sites at this location. Following the same trends as Camp Island, Holbourne corals also have an increased pattern of sediment found on corals, some predation and disease but with little measurable damage as a result.
Holbourne Island has comparatively very low macroalgae cover, and on average double the hard coral cover of Camp Island. However, TC Debbie was shown to have had a devastating impact on coral cover, with a loss of more than 75% of coral cover. Recovery of these communities remains, to-date, negligible.
The major regional scale bleaching event in early 2020 led to significant bleaching of Holbourne Island hard corals communities but to a lesser extent than at Camp Island; likely in part due to the slightly deeper sites at this location. Following the same trends as Camp Island, Holbourne corals also have an increased pattern of sediment found on corals, some predation and disease but with little measurable damage as a result.
Inshore corals and benthic (seafloor) cover are, to an extent, naturally acclimatised to greater frequency and scale of disturbances like cyclones, high water temperatures, and freshwater influx and elevated turbidity (sediment in water) from flooding compared to their more offshore counterparts. Measuring coral cover, alongside diversity, juvenile recruitment, and bleaching and disease, can help us to understand the typical degree of change in these communities, anticipate recovery potential and timeframes from such disturbances.
Surveys at Abbot Point commenced in 2016. A clear impact from Tropical Cyclone Debbie was shown 18 months later at Holbourne Island, which was most affected, given the cyclone's trajectory. Holbourne Island has struggled to recover from these impacts and has been predated consistently by crown-of-thorns starfish.
Holbourne Island sites were revised in 2020 and therefore trends shown are not temporally comparable. Nonetheless, changes observed since October 2020 show stable hard coral cover at all Holbourne Island sites.
Camp Island hard coral communities were somewhat protected by the angle of approach of Tropical Cyclone Debbie and showed strong recovery since 2017. The 2020 summer bleaching event was found to significantly affect corals at all sites with close to 40% of coral bleached and a high percentage of mortality at Camp Island (cover reduced from 24% to 6% from October 2019 to October 2020). Signs of recovery at Camp Island have since been observed however cover is still significantly below levels seen in 2019.
You can see more analysis on the data in these reports.
Surveys at Abbot Point commenced in 2016. A clear impact from Tropical Cyclone Debbie was shown 18 months later at Holbourne Island, which had approximately 14% soft coral cover prior to this and has struggled to recover above 2-3% since.
Camp Island communities however have never recorded high percentages of soft coral cover, being dominated by hard corals, such as the fast-growing Acropora spp. corals and Montipora spp. (collectively more than 70% of hard coral coverage).
You can see more analysis of the data in these reports.
Holbourne Island is a more mid-shelf location than Camp Island. In part due to its location, Holbourne Island has never shown levels of macroalgae >1%. Cover during the most recent pre-wet surveys was 0.32%.
Camp Island, by comparison, has consistently had much higher macroalgae cover, 35.5% during the same recent survey period. These high macroalgae levels are thought to be influenced by seasonal nutrient fluctuations. The peak of 76% in October 2020 followed the GBR region-wide accumulated heat stress event of early 2020. In the Mackay and Hay Point region, macroalgae were seen over this same period to decline significantly except for Sargassum spp., the predominant macroalgae at Camp Island.
While Camp Island coral communities have historically been more susceptible to the stress-related bleaching from high water temperatures and competition for space with macroalgae, the main influences on coral health at Holbourne Island are predation by sea snails (Drupella) and crown-of-thorns starfish.
You can see more analysis on the data in these reports.