Marine Protected Areas are increasingly becoming a tool of choice for conservation and management of marine resources and ecosystems. Data on biodiversity are necessary to assist in establishing protected areas for conservation objectives to be met. Toward that effect, we investigated reef biodiversity patterns in three large-scale coastal regions of Brazil. The study areas comprised of an upwelling region, an adjacent high impacted region, and a more distant marine park. We surveyed four reef sites in each study region. Species counts of sessile benthic organisms, substrate relief, and average monthly water temperatures were recorded during the surveys. Benthic organisms were identified to the lowest taxa possible using still photos. Biodiversity was estimated using Shannon’s index on richness of organism taxa. Diversity was highest at the upwelling and high-impacted areas. No substrate relief patterns were found. Temperature readings showed lower average values at the upwelling and high impacted regions. Our results favor the upwelling region for establishment of a Marine Protected Area. Moreover, the similar diversity between the upwelling and the high impacted regions showed evidence of spillover effects from the former into the latter region, further demonstrating the importance of the former region for conservation.
References
[1]
Kaplan, K., Hart, D., Hopkins, K., Gallager, S., York, A., Taylor, R. and Sullivan, P. (2017) Invasive Tunicate Restructures Invertebrate Community on Fishing Grounds and a Large Protected Area on Georges Bank. Biological Invasions, 20, 87-103. https://doi.org/10.1007/s10530-017-1517-y
[2]
Ban, N., Davies, T., Aguilera, S., Brooks, C., Cox, M., Epstein, G., Evans, L., Maxwell, S. and Nenadovic, M. (2017) Social and Ecological Effectiveness of Large Marine Protected Areas. Global Environmental Change, 43, 82-91.
https://doi.org/10.1016/j.gloenvcha.2017.01.003
[3]
Friedlander, A., Golbuu, Y., Ballesteros, E., Caselle, J., Gouezo, M., Olsudong, D. and Sala, E. (2017) Size, Age, and Habitat Determine Effectivenss of Palau’s Marine Protected Areas. PLOS ONE, 12, e0174787.
https://doi.org/10.1371/journal.pone.0174787
[4]
Welch, H., Pressey, R. and Reside, A. (2018) Using Temporally Explicit Habitat Suitability Models to Assess Threats to Mobile Species and Evaluate the Effectiveness of Marine Protected Areas. Journal of Nature Conservation, 41, 106-115.
https://doi.org/10.1016/j.jnc.2017.12.003
[5]
Nicoll, R. and Day, J. (2017) Correct Application of the IUCN Protected Area Management Categories to the CCAMLR Convention Area. Marine Policy, 77, 9-12.
https://doi.org/10.1016/j.marpol.2016.11.035
[6]
Mellin, C., MacNeil, M., Cheal, A., Emslie, M. and Caley, M. (2016) Marine Protected Areas Increase Resilience among Coral Reef Communities. Ecology Letters, 19, 626-637. https://doi.org/10.1111/ele.12598
[7]
Cabral, R., Gaines, S., Lim, M., Atrigenio, M., Mamauag, S., Pedemonte, G. and Alino, P. (2017) Siting Marine Protected Areas Based on Habitat Quality and Extent Provides the Greatest Benefit to Spatially Structured Metapopulations. Ecosphere, 7, e01533. https://doi.org/10.1002/ecs2.1533
[8]
Cox, C., Valdivia, A., McField, M., Castillo, K. and Bruno, J. (2017) Establishment of Marine Protected Areas Alone Does Not Restore Coral Reef Communities in Belize. Marine Ecology Progress Series, 563, 65-79.
https://doi.org/10.3354/meps11984
[9]
Visconti, P. and Elkin, C. (2009) Using Connectivity Metrics in Conservation planning—When Does Habitat Quality Matter? Diversity and Distributions, 15, 602–612. https://doi.org/10.1111/j.1472-4642.2009.00564.x
[10]
Lima, I., Garcia, C. and Moller, O. (1996) Ocean Surface Processes on the Southern Brazilian Shelf: Characterization and Seasonal Variability. Continental Shelf Research, 16, 1307-1317. https://doi.org/10.1016/0278-4343(95)00066-6
[11]
Andrello, M., Mouillot, D., Somot, S., Thuiller, W. and Manel, S. (2014) Additive Effects of Climate Change on Connectivity between Marine Protected Areas and Larval Supply to Fishes Areas. Diversity and Distributions, 21, 139-150.
https://doi.org/10.1111/ddi.12250
[12]
Colleter, M., Gascuel, D., Albouy, C., Francour, P., Morais, L., Valls, A. and Le Loch, F. (2014) Fishing Inside or Outside? A Case Study Analysis of Potential Spillover Effect from Marine Protected Areas Using Food-Web Models. Journal of Marine Systems, 139, 383-395. https://doi.org/10.1016/j.jmarsys.2014.07.023
[13]
Di Lorenzo, M., Claudet, J. and Guidetti, P. (2016) Spillover from Marine Protected Areas to Adjacent Fisheries Has an Ecological and Fishery Component. Journal for Nature Conservation, 32, 62-66. https://doi.org/10.1016/j.jnc.2016.04.004
[14]
Cuervo-Sanchez, R., Madonado, J. and Rueda, M. (2018) Spillover from Marine Protected Areas on the Pacific Coast in Colombia: A Bioeconomic Modeling Approach for Shrimp Fisheries. Marine Policy, 88, 182-188.
https://doi.org/10.1016/j.marpol.2017.10.036
[15]
Summerhayes, C., Melo, U. and Barretto, H. (1976) The Influence of Upwelling on Suspended Matter and Shelf Sediments Off Southeastern Brazil. Journal of Sedimentary Research, 46, 819-828.
[16]
Ding, B., Curole, J., Husemann, M. and Danley, P. (2014) Habitat Complexity Predicts the Community Diversity of Rock-Dwelling Cichlid Fish in Lake Malawi, East Africa. Hydrobiologia, 748, 133-143. https://doi.org/10.1007/s10750-014-1932-3
[17]
Oyugi, D., Mavuti, K., Aloo, P., Ojuok, J. and Britton, J. (2014) Fish Habitat Suitability and Community Structure in the Equatorial Lake Naivasha, Kenya. Hydrobiologia, 727, 51-63. https://doi.org/10.1007/s10750-013-1785-1
[18]
Martelo, J., Grossman, G., Porto, M. and Magalhaes, M. (2014) Habitat Patchiness Affects Distribution and Microhabitat Use of Endangered Mira Chub Squaliustorgalensis (Actimopterygii, Cypriniformes). Hydrobiologia, 732, 93-109.
https://doi.org/10.1007/s10750-014-1850-4
