Spatial variation in sea urchins, fish predators, and bioerosion rates on coral reefs of Belize

Coral Reefs ◽  
2006 ◽  
Vol 26 (1) ◽  
pp. 71-78 ◽  
Author(s):  
Jocelyn Brown-Saracino ◽  
Paulette Peckol ◽  
H. Allen Curran ◽  
Martha L. Robbart
2014 ◽  
Vol 136 (4) ◽  
pp. 2276-2276 ◽  
Author(s):  
Simon E. Freeman ◽  
Lauren A. Freeman ◽  
Marc O. Lammers ◽  
Michael J. Buckingham

2016 ◽  
Vol 140 (4) ◽  
pp. 3018-3019
Author(s):  
Eden Zang ◽  
Marc Lammers ◽  
Max Kaplan ◽  
T. A. Mooney ◽  
Pollyanna Fisher-Pool ◽  
...  

2011 ◽  
Vol 2011 ◽  
pp. 1-8 ◽  
Author(s):  
Leor Korzen ◽  
Alvaro Israel ◽  
Avigdor Abelson

Herbivory is an important structuring factor in coral reefs, influencing seaweed abundance, competitive interactions between seaweeds and corals, and coral reef resilience. Despite reports of a drastic increase in the cover of benthic algae and turf dominancy in the coral reefs of Eilat, Red Sea, very little is known about the factors responsible for this phenomenon or the possible effects of herbivory on turf algae and coral recruits. Here, we examine the effects of herbivory by experimentally exposing turf algae and coral recruits to grazing activities of herbivorous fish and sea urchins. Using remote video cameras to document removal of algae and coral spats, we show that the main grazing impact is due to daily grazing by fishes, whereas the significant impact of sea urchins is mainly expressed in their adverse effect on the survival of coral recruits, with a relatively low effect on algal biomass. These findings contribute to our understanding of the factors influencing turf algae establishment and proliferation, and the survival of coral recruits on the coral reefs of Eilat. The clear differences between the impact of herbivorous fish and that of sea urchins, on the Eilat reefs, have critical implications for reef resilience and restoration measures.


2002 ◽  
Vol 29 (4) ◽  
pp. 460-483 ◽  
Author(s):  
Timothy R. McClanahan

In this paper the current status of coral reefs, predictions concerning the ecological state of coral reefs to the 2025 time horizon and the research needs that can help understanding and management activities that might alleviate detrimental ecological changes are evaluated and discussed. The present rate of CO2 emissions will produce an atmospheric concentration in 100 years not experienced during the past 20 million years and water temperatures above those of the past interglacial 130 000 years before present. Human influences on water temperatures, seawater chemistry (toxic substances, nutrients and aragonite saturation), the spread of diseases, removal of species and food web alterations are presently changing reef ecology. A significant ecological reorganization is underway and changes include a reduction in calcifying and zooxanthellae-hosting organisms, their obligate symbionts, and species at higher trophic levels, with an increase in generalist species of low trophic level that are adapted to variable environments. Late-successional fleshy brown algae of low net productivity or non-commercial invertebrates such as sea urchins, starfish and coral-eating snails will dominate many reefs. These changes will be associated with a loss of both net benthic and fisheries production and inorganic carbonate deposition; this will reduce reef complexity, species richness, reef growth and increase shoreline erosion. To avert these changes management is needed at both global and local levels. Both levels need to reduce greenhouse gases and other waste emissions and renew efforts to improve resource management including restrictions on the use of resources and globalization of resource trade, run-off and waste production, and balancing potential reef production and resource consumption.


2017 ◽  
Vol 3 (2) ◽  
pp. 134
Author(s):  
Tiara Permata Sari ◽  
Abd. Rahman As-syakur ◽  
Yulianto Suteja ◽  
Dwi Budi Wiyanto

Marine intertidal region is an area that is affected by the mainland. One of the ecosystems found in the intertidal area is the coral reef ecosystem. Urchin is one that lives on these ecosystems. Sanur Beach area has coral reefs and the intertidal zone is quite extensive. The many activities and cruise tourism in Sanur Beach will indirectly affect the life of coral reefs and associated animal in it in this case urchins. The purpose of this study was to determine the relationship density of sea urchins and coral reefs cover percentage in the intertidal area on Sanur Beach. Research done during low tide. Coral reef data collection method and the density of sea urchins using 5x5m quadratic transects were analyzed using Pear Person bivariate correlations. Urchin densities ranging between 0-2.04 ind/m2. The percentage cover coral reefs ranged from 0.1- 17.9%. High and low density of sea urchins and the percentage of coral reefs affected allegedly incompatibility place their lives and because of pressure from community activities in Sanur. The density of sea urchins and the percentage of coral cover has a significant relationship with a strong degree of correlation is 0.79. Positive direction on that relationship means that the higher percentage of coral reefs, the higher density of sea urchins. This assume in which they live almost the same that is in need of a hard substrate and urchins use of coral reefs as a shelter.


2018 ◽  
Vol 39 (5(SI)) ◽  
pp. 825-834 ◽  
Author(s):  
M. Aminur Rahman ◽  
◽  
Y. Arakaki ◽  
Sang-Go Lee ◽  
Fatimah Md. Yusoff ◽  
...  

Author(s):  
Levy D. Obonaga ◽  
Mauro Giovanni Zucconi ◽  
Edgardo Londoño-Cruz

Echinoids are an important component of benthic communities; they can directly modify the distribution and relative abundance of algae and corals as well as be an agent in the process of bioerosion. Despite research on echinoids in the Colombian Pacific, the bioerosion rate due to grazing by Diadema mexicanum on the coral reefs of Gorgona Island remains unknown. Therefore,considering the relative high abundance of this echinoid and its potential negative effects on coral reefs, the main objective of this study was to determine the rate of bioerosion. To accomplish this, 1-m2 quadrats were randomly established in each of three reef zones (at lowtide, Backreef: ±1 m depth, Reef plain: ±0.5 m and Reef front: ±3.0 m) of La Azufrada fringing reef (Gorgona Island National Natural Park). Sea urchins were counted and measured (test diameter) inside the quadrats, and 30 urchins per zone (90 in total) were collected toestimate the bioerosion rate. The average sea urchin density and size (±SD) were 8.28±11.65 ind/m2 and 19.62±5.02 mm, respectively. The average bioerosion rate for the reef was 0.083 kg CaCO3/m2/yr, and it was significantly affected by echinoid size (p<0.001) and reefzone (p=0.0002). Additionally, a direct relationship was observed between intestinal calcium carbonate (CaCO3) and depth (p=0.043) and size (p<0.001). Finally, although large sea urchins may have important effects, it is unlikely that the bioerosion caused by D. mexicanumpresents a threat to La Azufrada fringing reef due to its low relative abundance; this is reflected by the relatively low bioerosion rate relative to other reefs in the Tropical Eastern Pacific.


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