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Widespread loss of Caribbean acroporid corals was underway before coral bleaching and disease outbreaks.
Cramer KL
,
Jackson JBC
,
Donovan MK
,
Greenstein BJ
,
Korpanty CA
,
Cook GM
,
Pandolfi JM
.
Abstract
The mass mortality of acroporid corals has transformed Caribbean reefs from coral- to macroalgal-dominated habitats since systematic monitoring began in the 1970s. Declines have been attributed to overfishing, pollution, sea urchin and coral disease, and climate change, but the mechanisms are unresolved due to the dearth of pre-1970s data. We used paleoecological, historical, and survey data to track Acropora presence and dominance throughout the Caribbean from the prehuman period to present. Declines in dominance from prehuman values first occurred in the 1950s for Acropora palmata and the 1960s for Acropora cervicornis, decades before outbreaks of acroporid disease or bleaching. We compared trends in Acropora dominance since 1950 to potential regional and local drivers. Human population negatively affected and consumption of fertilizer for agriculture positively affected A. palmata dominance, the latter likely due to lower human presence in agricultural areas. The earlier, local roots of Caribbean Acropora declines highlight the urgency of mitigating local human impacts.
Fig. 1. Distribution of dominance and presence/absence data for acroporid corals.Data from reef crest zones in magenta; data from midslope zones in blue. Size of dot proportional to total number of surveys across both reef zones and all bins combined (range, 1 to 541).
Fig. 2. Long-term trends in presence and dominance of Caribbean acroporid corals.Proportion of reef sites with species present (gray) and dominant (black), determined from a binomial GLMM that included country as a random effect. Vertical bars are standard errors of mean-fitted values; stars indicate earliest significant declines since the historical period compared with Pleistocene values; numbers are reef sites with species presence/absence data for each time bin. Arrows indicate first recorded occurrence of major novel disturbances, with timing of coral bleaching signifying bleaching at several locations across the Caribbean. Diadema, mass die-off of sea urchin D. antillarum.
Fig. 3. Significant drivers of change in dominance of A. palmata at the reef crest zone from 1950 to 2011.(A) Effect of human population density. (B) Effect of fertilizer consumption. Partial effects determined from a binomial generalized linear mixed effects model that included time bin and country as random effects. Fixed effects were log transformed to reduce the influence of extreme large values and improve model convergence. Blue bands represent 95% confidence intervals.
Alvarez-Filip,
Flattening of Caribbean coral reefs: region-wide declines in architectural complexity.
2009, Pubmed,
Echinobase
Alvarez-Filip,
Flattening of Caribbean coral reefs: region-wide declines in architectural complexity.
2009,
Pubmed
,
Echinobase
Bolker,
Generalized linear mixed models: a practical guide for ecology and evolution.
2009,
Pubmed
Cramer,
Anthropogenic mortality on coral reefs in Caribbean Panama predates coral disease and bleaching.
2012,
Pubmed
Cramer,
Prehistorical and historical declines in Caribbean coral reef accretion rates driven by loss of parrotfish.
2017,
Pubmed
,
Echinobase
Donner,
Global assessment of coral bleaching and required rates of adaptation under climate change.
2005,
Pubmed
Fernandez,
A literature review on trace metals and organic compounds of anthropogenic origin in the Wider Caribbean Region.
2007,
Pubmed
Gardner,
Long-term region-wide declines in Caribbean corals.
2003,
Pubmed
Highsmith,
Survival of hurricane-generated coral fragments and a disturbance model of reef calcification/growth rates.
1980,
Pubmed
Hughes,
Catastrophes, phase shifts, and large-scale degradation of a Caribbean coral reef.
1994,
Pubmed
Hughes,
Climate change, human impacts, and the resilience of coral reefs.
2003,
Pubmed
Hughes,
Phase shifts, herbivory, and the resilience of coral reefs to climate change.
2007,
Pubmed
Jackson,
Historical overfishing and the recent collapse of coastal ecosystems.
2001,
Pubmed
Lessios,
Spread of diadema mass mortality through the Caribbean.
1984,
Pubmed
,
Echinobase
Loh,
Indirect effects of overfishing on Caribbean reefs: sponges overgrow reef-building corals.
2015,
Pubmed
Pandolfi,
Global trajectories of the long-term decline of coral reef ecosystems.
2003,
Pubmed
Pandolfi,
Ecological persistence interrupted in Caribbean coral reefs.
2006,
Pubmed
Perry,
Regional-scale dominance of non-framework building corals on Caribbean reefs affects carbonate production and future reef growth.
2015,
Pubmed
Rasher,
Chemically rich seaweeds poison corals when not controlled by herbivores.
2010,
Pubmed
Sheppard,
Sea surface temperature 1871-2099 in 38 cells in the Caribbean region.
2005,
Pubmed
Smith,
Indirect effects of algae on coral: algae-mediated, microbe-induced coral mortality.
2006,
Pubmed
Sutherland,
Human sewage identified as likely source of white pox disease of the threatened Caribbean elkhorn coral, Acropora palmata.
2010,
Pubmed