Abstract

In 2005, an extreme heatwave hit the Wider Caribbean, followed by 13 hurricanes (including hurricanes Emily and Wilma) that caused significant loss in hard coral cover. However, the drivers of the potential recovery are yet to be fully understood. Based on recent findings in the literature of coral cover recovery in the Mexican Caribbean after the mass bleaching event and associated hurricanes in 2005, this study analyzed, through random-effects meta-analysis, the hard coral and macroalgae benthic development and potential drivers of change between 2005 and 2016 in the Mexican Caribbean. Therefore, we tested the relative effect of sea surface temperature (SST), chlorophyll-a water concentration, coastal human population development, reef distance to shore, and geographical location on both hard coral and macroalgae cover over time. Findings revealed increases of both hard coral (by 6%) and algae cover (by ca. 14%, i.e., almost three times the increase of corals) over 12 years. Although our findings confirm the partial coral recovery after the 2005 Caribbean mass coral mortality event, they also indicate rapid colonization of algae across the region. Surprisingly, only SST correlated negatively with changes in coral cover. Contrary to expectations, there was a significantly greater algae cover increase in the Central section of the Mexican Caribbean, which is characterized by a low population density. However, a constant discharge of nutrient-rich freshwater may have facilitated algae growth there. This study reports partial regional reef recovery, but it also indicates that local factors, particularly eutrophication, facilitate algae growth at a speed that is much faster than coral recovery.

Highlights

  • Worldwide, coral reefs are jeopardized through a combination of natural and anthropogenic pulse disturbances

  • (Figure 2, Supplementary Materials, Figures S10 and S11). This corresponds to a coral cover increase of

  • The Sea Surface Temperate (SST) increased along the coast of Quintana Roo (Figure 3a)

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Summary

Introduction

Coral reefs are jeopardized through a combination of natural and anthropogenic pulse disturbances. Some reefs around the world show coral recovery after such mass mortality events [4,5,6,7,8,9] For instance, corals in the Eastern Tropical Pacific recovered by 30% in 13 years after the El Niño phenomenon in 1982–1983 [7]. In 13 years after the 1998 bleaching event [8]. The North-Western Australian reefs showed a 35% coral cover recovery within 12 years after the 1998 bleaching event [6]. High herbivore grazing capacity [6,10,12], high coral and fish diversity [13], and isolation from chronic anthropogenic pressures [13] can enhance coral recovery

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