State of corals and coral reefs of the Galápagos Islands (Ecuador): Past, present and future. (August 2018)

• Record Type: Journal Article
• Authors: Glynn, Peter W.; Feingold, Joshua S.; Baker, Andrew; Banks, Stuart; Baums, Iliana B.; Cole, Julia; Colgan, Mitchell W.; Fong, Peggy; Glynn, Peter J.; Keith, Inti; Manzello, Derek; Riegl, Bernhard; Ruttenberg, Benjamin I.; Smith, Tyler B.; Vera-Zambrano, Mariana
• Is Part Of: Marine pollution bulletin. Volume 133(2018)
• Page Start: 717
• Page End: 733
• Publication Date: 2018-08
• Subjects: El Niño-Southern Oscillation -- Echinoid bioerosion -- Coral recovery -- Coral loss -- Caulerpa -- Overfishing -- Galápagos National Park; Marine pollution -- Periodicals; Marine Biology -- Periodicals; Water Pollution -- Periodicals; Mer -- Pollution -- Périodiques; Publications périodiques; Pollution des mers; Lutte antipollution; Electronic journals; 363.7394
• DOI: 10.1016/j.marpolbul.2018.06.002
• Languages: English
• ISSNs: 0025-326X

Abstract

Abstract: Coral populations and structural coral reefs have undergone severe reductions and losses respectively over large parts of the Galápagos Islands during and following the 1982–83 El Niño event. Coral tissue loss amounted to 95% across the Archipelago. Also at that time, all coral reefs in the central and southern islands disappeared following severe degradation and eventual collapse due primarily to intense bioerosion and low recruitment. Six sites in the southern islands have demonstrated low to moderate coral community (scattered colonies, but no carbonate framework) recovery. The iconic pocilloporid reef at Devil's Crown (Floreana Island) experienced recovery to 2007, then severe mortality during a La Niña cooling event, and is again (as of 2017) undergoing rapid recovery. Notable recovery has occurred at the central (Marchena) and northern islands (Darwin and Wolf). Of the 17 structural reefs first observed in the mid-1970s, the single surviving reef (Wellington Reef) at Darwin Island remains in a positive growth mode. The remainder either degraded to a coral community or was lost. Retrospective analyses of the age structure of corals killed in 1983, and isotopic signatures of the skeletal growth record of massive corals suggest the occurrence of robust coral populations during at least a 500-year period before 1983. The greatest potential threats to the recovery and persistence of coral reefs include: ocean warming and acidification, bioerosion, coral diseases, human population growth (increasing numbers of residents and tourists), overfishing, invasive species, pollution, and habitat destruction. Such a diverse spectrum of disturbances, acting alone or in combination, are expected to continue to cause local and archipelago-wide mortality and degradation of the coral reef ecosystem.