Revista de Biología Tropical ISSN Impreso: 0034-7744 ISSN electrónico: 2215-2075

OAI: https://revistas.ucr.ac.cr/index.php/rbt/oai
Marine Protected Area monitoring in the nearshore waters of Grenada, Eastern Caribbean: benthic cover and fish populations
PDF
HTML

Keywords

benthic cover
reef fish
monitoring
Grenada
Eastern Caribbean
marine protected area
cubierta bentónica
peces de arrecife
monitoreo
Granada
área protegida del Caribe
Marina oriental

How to Cite

Anderson, R., Morrall, C., Jossar, J., Nimrod, S., Bolda, E., Musser, K., Berg, C., & Balza, R. (2014). Marine Protected Area monitoring in the nearshore waters of Grenada, Eastern Caribbean: benthic cover and fish populations. Revista De Biología Tropical, 62(S3), 273–286. https://doi.org/10.15517/rbt.v62i0.15922

Abstract

Grenada is highly dependent on coral reefs as a source of food and to support tourism. Local and global environmental stressors threaten these reefs. Legislation was created for this MPA in 2001, permanent mooring buoys were deployed in 2009 and enforcement of fishing restrictions began in 2010. Initiatives to address point and nonpoint source pollution from the land have recently begun, aimed at reducing stress on reef area. This study documents benthic cover and fish populations associated with reefs in a Marine Protected Area (MPA) along Grenada’s southwest coast from 2008 through 2012. Both Point Line Intercept and Photo Quadrat methods were used to assess benthic cover along permanent 30m transects (8 in and 12 outside the area) annually. Fish and Diadema antillarum urchin relative abundance were determined based on 2m wide belt surveys along the same transects. The predominant substrate cover was algae, ranging from 41% in 2009 to 74.2% in 2011. A general trend of increasing algal cover was noted. Combined annual survey results prior (2008-2010) and after controls were implemented (2011-2012) showed a significant increase in algal cover. The predominant algal form was macroalgae comprising 65.4% - 90.8% of total algae. Live hard coral percent cover ranged from 8.7% to 21.1%. Little annual variation was observed in percent live coral cover. Branching corals (34.1% - 52.3% of total living hard coral) were the most common. Of the 19 living hard coral species identified, Porites porites (21%-23%) and Porites astreoides (20%) dominated percentage composition. Madracis mirabilis contributed 21% of total live hard coral outside the MPA but only 8.7% in the MPA. Of the 63 species of fish identified in the study areas Chromis spp. (71.5% - 46%) was the dominant group. Wrasse had a significant increase from 6.9% in 2008 to 21.5% in 2010 inside the MPA with a similar increase peaking in 2011 outside the MPA. There was a noticeable (though not statistically significant) increase in piscivorous fishes in the MPA in 2012. This is a promising indication that fishing restrictions in the MPA may be having an effect. Diadema antillarum density was low, ranging from 4.58 to 0.21 urchins/100m2 outside and 0.28 to 0.10 urchins/100m2 inside despite a stocking attempt in the area in 2011. Rev. Biol. Trop. 62 (Suppl. 3): 273-286. Epub 2014 September 01.

 

https://doi.org/10.15517/rbt.v62i0.15922
PDF
HTML

References

Alvarado, J. J., Cortés J., Esquivel M. F., & Salas, E. (2012). Costa Rica’s Marine Protected Areas: status and perspectives. Revista de Biologia Tropical, 60, 129-142.

Anderson, R., Morrall C., Nimrod S., Balza R., Berg C., & Jossart, J. (2012). Benthic and fish population monitoring in the nearshore waters of Grenada, Eastern Caribbean. Revista de Biologia Tropical, 60, 71-87.

Angulo-Valdes, J. A., & Hatcher, B. C. (2010). A new typology of benefit derived from marine protected areas. Marine Policy, 34, 635-644.

Baker, A. C., Glynn P. W., & Riegl, B. (2008). Climate change and coral reef bleaching: an ecological assessment of long-term impacts, recovery trends and future outlook. Estuarine, Coastal and Shelf Science, 80, 435-471.

Bruckner, A.W., & Hill, R. (2009). Ten years of change to coral communities off Mona and Desecheo Islands, Puerto Rico from disease and bleaching. Diseases of Aquatic Organisms, 87, 19-31.

Buddemeier, R.W., Lane, D.R., & Martinich, J. A. (2011). Modeling regional coral reef responses to global warming and changes in ocean chemistry: Caribbean case study. Climatic Change, 109, 375-397.

Burke, L., & Maidens J. (2004). Reefs at risk in the Caribbean. Washington, D.C., USA: World Resources Institute.

Burke, L., Reytar, K., Spalding M., & Perry, A. (2011). Reefs at Risk Revisited. Washington, D.C., USA: World Resources Institute.

Byrne, J. (2007). Grenada Gap Analysis. Christiansted, St. Croix, USVI. 25: The Nature Conservancy.

Cantin, N. E., Cohen, A. L., Karnauskas, K. B., Tarrant, A. M., &. McCorkle, D. C. (2010). Ocean warming slows coral growth in the central Red Sea. Science, 329, 322-325.

Convention on Biological Diversity. (2012). Action Plan for Implementing the Convention on Biological Diversity’s Programme of Work on Protected Areas (Grenada). Retrieved from http://www.cbd.int/protected/implementation/actionplans/country/?country=gd

Crabbe, M. (2013). Coral Reef Populations in the Caribbean: Is There a Case for Better Protection against Climate Change? American Journal of Climate Change, 2(2), 97-105.

Crosby, M. P., & Reese E. S. (1996). A manual for monitoring coral reefs with indicator species: butterfly fishes as indicators of change on the Indo-Pacific reefs. NOAA, Silver Spring, Maryland, USA: Office of Ocean and Coastal Resource Management,

Eakin, C. M., Morgan J. A., Heron S. F., Smith T. B, Liu G., Alvarez-Filip, L., Baca, B., Bartels, E. Bastidas, C., …, & Yusuf, Y. (2010). Caribbean corals in crisis: record thermal stress, bleaching, and mortality in 2005. PLoS ONE, 5, e13969.

Fine, M. & Tchernov, D. (2007). Scleractinian coral species survive and recover from decalcification. Science, 315, 1811.

Gardner, T. A., Côte´, I. M., Gill, J. A., Grant, A., & Watkinson A. R. (2003). Long term region-wide declines in Caribbean corals. Science, 301, 958-960.

Graham, J. E., Barrett, N. S., & Stuart-Smith R. D. (2009). Exploited reefs protected from fishing transform over decades into conservation features otherwise absent from seascapes. Ecological Application, 19, 1967-1974.

Guarderas, A. P., Hacker, S. D., & Lubchenco, J. (2008). Current Status of Marine Protected Areas in Latin America and the Caribbean. Conservation Biology, 22, 1630-1640.

Humann, P. (1993). Reef Coral Identification (Florida, Caribbean, Bahamas). Jacksonville: New World Publications.

Jackson, J., Cramer, K. Donovan, M., Friedlander A., Hooten, A., & Lam, V. (2012). Tropical Americas Coral Reef Resilience Workshop - 2012. GCRMN Technical Report. Panama City, Panama: Smithsonian Tropical Research Institute.

Kelleher, G. (1999). Guidelines for Marine Protected Areas. IUCN - The World Conservation Union. Series 3.

Knowlton, N., & Jackson J. (2008). Shifting Baselines, Local Impacts, and Global Change on Coral Reefs. PLoS Biology, 6(2), e54.

Kohler, K. E., & Gill, S.M. (2006). Coral Point Count with excel extensions (CPCe): A visual basic program for the determination of coral and substrate coverage using random point count methodology. Computers & Geosciences, 32, 1259-1269

Littler, M. M., & Littler, D. S. (2007). Assessment of coral reefs using herbivory, nutrient assays and indicator groups of benthic primary producers: a critical synthesis, proposed protocols, and critique of management strategies. Aquatic Conservation: Marine and Freshwater Ecosystems, 17, 195-215.

Nimrod, S. (2012). The effectiveness of Diadema in triggering a phase shift reversal. Mini-Symposia presentation 12th ICRS, Cairns, Australia

Riegl, B., Bruckner, A., Coles, S., Renaud, P., & Dodge, R. E. (2009). Coral Reefs - Threats and conservation in an era of global change. Ann. NY Academic of Science, 1162, 136-186.

Riegl, B., Berumen, M., & Bruckner, A. (2013). Coral population trajectories, increased

disturbance and management intervention: a sensitivity analysis. Ecology & Evolution, 3(4), 1050-1064

Ries, J. B., Stanley S. M., & Hardie, L. A. (2006). Scleractinian corals produce calcite, and grow more slowly, in artificial Cretaceous seawater. Geology, 34, 525-528.

Sala, E., Costello, C., Dougherty, D., Heal, G., Kelleher, K., Murray, J., Rosenberg, A., & Sumaila, R. (2013). A General Business Model for Marine Reserves. PLoS ONE, 8(4), e58799.

Sandin, S. A., Sampayo E. M., & Vermeij, M. J. (2008). Coral reef fish and benthic community structure of Bonaire and Curaçao, Netherlands Antilles. Caribbean Journal of Science, 44, 137-144.

Selig, E. R., & Bruno, J. F. (2010). A Global Analysis of the Effectiveness of Marine Protected Areas in Preventing Coral Loss. PLoS ONE, 5(2), e9278.

Sokal, R. R., & Rohlf, F. J. (1995). Biometry: The principles and practice of statistics in biological research. 3rd edition. New York: W.H. Freeman.

Sprung, J. (1999). Oceanographic Series Corals: A Quick Reference Guide. Miami: Ricordia Publishing.

Turner, M. (2009). Draft Grenada Protected Area System Plan Part 1 - Identification and Designation of Protected Areas. Prepared for the Environment and Sustainable Development Unit (ESDU) of the Organization of Eastern Caribbean States (OECS) Protected Areas and Associated Livelihoods (OPAAL) Project.

Wiedenmann, J., D’Angelo, C., Smith, E. G., Hunt, A. N., Legiret, F. E., Postle, A. D., & Achterberg, E. P. (2013). Nutrient enrichment can increase the susceptibility of reef corals to bleaching. Nature and Climate Change, 3, 160-164.

Comments

Creative Commons License

This work is licensed under a Creative Commons Attribution 4.0 International License.

Copyright (c) 2014 Revista de Biología Tropical

Downloads

Download data is not yet available.