Journal
REGIONAL STUDIES IN MARINE SCIENCE
Volume 8, Issue -, Pages 422-429Publisher
ELSEVIER SCIENCE BV
DOI: 10.1016/j.rsma.2016.05.005
Keywords
Reef rehabilitation; Coastal management; Artificial reefs; Coral nurseries; Transplantation
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Funding
- Wildlife Reserves Singapore Conservation Fund
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Singapore's coral reefs have been exposed to five decades of increased sedimentation that reduced underwater visibility from over 10 m in the early 1960s to under 2 m today. The lower depth limit of scleractinian coral growth moved up from 10m to 6 m, while live coral cover decline is less apparent now than in the early decades of augmented sediment loading. Coral community structure has changed with dominance shifting to more low-light tolerant species such as those of the genera Pectinia and Turbinaria. Reef restoration to increase coral cover of degraded reefs and initiate colonisation of non-reef areas is considered to be viable following observations of predictable mass spawning events, recruitment and vigorous growth, but the techniques employed need to account for the high sediment conditions and destabilised reef substrate. The deployment of fibreglass artificial reef units increased opportunities for coral establishment, and supported at least 106 reef taxa, including 29 scleractinian genera after 10 years. As vital components of restoration, coral nurseries comprising mesh-net platforms raised above the reef floor prevented sediment accumulation and smothering, and enabled the rearing of coral fragments and juveniles with reduced mortality. This included the nurturing of 'corals of opportunity' (naturally fragmented pieces of live coral lying on the reef bed as well as recruits settled on loose rubble), which would otherwise be killed by sedimentation. Transplants of massive or encrusting species displayed higher survival over branching ones. Restoration strategies need to be adapted to changed environmental conditions caused by anthropogenic disturbances. (C) 2016 Elsevier B.V. All rights reserved.
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