Click
here to close Hello! We notice that
you are using Internet Explorer, which is not supported by Echinobase
and may cause the site to display incorrectly. We suggest using a
current version of Chrome,
FireFox,
or Safari.
PeerJ
2020 Jan 01;8:e8428. doi: 10.7717/peerj.8428.
Show Gene links
Show Anatomy links
Lack of recovery of the long-spined sea urchin Diadema antillarum Philippi in Puerto Rico 33 years after the Caribbean-wide mass mortality.
Tuohy E
,
Wade C
,
Weil E
.
???displayArticle.abstract???
Caribbean populations of the long-spined black sea urchin Diadema antillarum Philippi were decimated by a disease-induced mass mortality in the early 1980''s. The present study provides an updated status of the D. antillarum recovery and population characteristics in La Parguera Natural Reserve, Puerto Rico. The last detailed study to assess population recovery in 2001, indicated a slow, and modest recovery, albeit densities remained far below pre-mass mortality levels. Population densities were assessed along three depth intervals in six reef localities and one depth in three lagoonal sea-grass mounds using ten 20 m2 (10 × 2 m) belt-transects at each depth interval. Most of these were previously surveyed in 2001. All individuals encountered along the belt transects were sized in situ with calipers and rulers to characterize the size (age) structure of each population and get insight into the urchin''s population dynamics and differences across localities in the area. Habitat complexity (rugosity) was assessed in all depth intervals. No significant differences in population densities between reef zones (inner shelf and mid-shelf) were observed, but significantly higher densities were found on shallow habitats (<5 m depth; 2.56 ± 1.6 ind/m2) compared to intermediate (7-12 m; 0.47 ± 0.8 ind/m2) and deep (>12 m; 0.04 ± 0.08 ind/m2) reef habitats in almost all sites surveyed. Habitat complexity had the greatest effect on population densities at all levels (site, zone and depth) with more rugose environments containing significantly higher densities and wider size structures. Comparison between survey years revealed that D. antillarum populations have not increased since 2001, and urchins seem to prefer shallower, more complex and productive areas of the reef. Populations were dominated by medium to large (5-9 cm in test diameter) individuals and size-frequency distributions indicated that smaller juveniles were virtually absent compared to 2001, which could reflect a recruitment-limited population and explain in part, the lack of increase in population densities. The limited temporal scale of this study, high horizontal movement of individuals along the complex, shallower reef and inshore habitats could also explain the general decline in mean densities. Other extrinsic factors affecting reproductive output and/or succesful recruitment and survival of juveniles likely contribute to the high variablility in population densities observed over time.
Figure 1. La Parguera Natural Reserve, Puerto Rico.Map of nearshore (NS-1-3), seagrass mounds (Coronas) and reef localities sampled. Exploratory surveys were conducted at nearshore (NS-1-3) and deep reef localities (Weinberg, Old Buoy and Black Wall). Inset shows relative location of La Parguera in relation to the island of Puerto Rico.
Figure 2. Comparison of Diadema antillarum densities between years and sampling localities.Data are mean densities (±SD) of D. antillarum in (A) each of the reefs and seagrass mounds sampled in this study and (B) each of the reef and seagrass mounds sampled in 2001 (Weil, Torres & Ashton, 2005). Mata La Gata and San Cristobal were not sampled in the 2001 study. The number of transects completed at each depth interval in the 2001 study are as follows: Corona 1, n = 8; Corona 2, n = 7; Corona 3, n = 5; Caracoles, n = 12 (0â5 m), n = 6 (7â12 m), n = 6 (>12 m); Enrigue, n = 6 (0â5 m), n = 6 (7â12 m), n = 0 (>12 m); Laurel, n = 8 (0â5 m), n = 4 (7â12 m), n = 0 (>12 m); Media Luna, n = 12 (0â5 m), n = 6 (7â12 m), n = 6 (>12 m). All data are individuals per m2.
Figure 3. Size frequency distributions of Diadema antillarum observed at each sampling location.Data are oral test diameter (cm) of D. antillarum collected and measured at (A) seagrass mounds, (B) Caracoles reef, (C) Laurel reef), (D) Enrique reef, (E) Media Luna reef, (F) Mata la Gata reef, and (G) San Cristobal reef.
Figure 4. Significant correlation between population densities of Diadema antillarum and habitat complexity (rugosity) were found at each reef site (Spearman rank correlation: rs = 0.178, p < 0.05).Data are the population density (ind./m2) and rugosity index recorded from transects at reef sites (n = 180).
Carpenter,
Local and regional scale recovery of Diadema promotes recruitment of scleractinian corals.
2006, Pubmed,
Echinobase
Carpenter,
Local and regional scale recovery of Diadema promotes recruitment of scleractinian corals.
2006,
Pubmed
,
Echinobase
Eakin,
Caribbean corals in crisis: record thermal stress, bleaching, and mortality in 2005.
2010,
Pubmed
Edmunds,
Recovery of Diadema antillarum reduces macroalgal cover and increases abundance of juvenile corals on a Caribbean reef.
2001,
Pubmed
,
Echinobase
Hay,
Competition between herbivourous fishes and urchins on Caribbean reefs.
1985,
Pubmed
,
Echinobase
Hernández,
The key role of the sea urchin Diadema aff. antillarum in controlling macroalgae assemblages throughout the Canary Islands (eastern subtropical Atlantic): an spatio-temporal approach.
2008,
Pubmed
,
Echinobase
Hertler,
Spatial variability associated with shifting land use: water quality and sediment metals in La Parguera, Southwest Puerto Rico.
2009,
Pubmed
Hoegh-Guldberg,
Coral reefs under rapid climate change and ocean acidification.
2007,
Pubmed
Hughes,
Catastrophes, phase shifts, and large-scale degradation of a Caribbean coral reef.
1994,
Pubmed
Hughes,
Global warming and recurrent mass bleaching of corals.
2017,
Pubmed
Lafferty,
Marine disease impacts, diagnosis, forecasting, management and policy.
2016,
Pubmed
Lessios,
Spread of diadema mass mortality through the Caribbean.
1984,
Pubmed
,
Echinobase
Lessios,
The Great Diadema antillarum Die-Off: 30 Years Later.
2016,
Pubmed
,
Echinobase
Oliver,
Contrasting responses of coral reef fauna and foraminiferal assemblages to human influence in La Parguera, Puerto Rico.
2014,
Pubmed
Ryan,
A record of recent change in terrestrial sedimentation in a coral-reef environment, La Parguera, Puerto Rico: a response to coastal development?
2008,
Pubmed
Weil,
Population characteristics of the sea urchin Diadema antillarum in La Parguera, Puerto Rico, 17 years after the mass mortality event.
2005,
Pubmed
,
Echinobase
Weil,
Yellow band disease compromises the reproductive output of the Caribbean reef-building coral Montastraea faveolata (Anthozoa, Scleractinia).
2009,
Pubmed
Weil,
Status and progress in coral reef disease research.
2006,
Pubmed