Faixa marginal de proteção de lagoas costeiras - O estudo de caso da Lagoa de Araruama.

A Lagoa de Araruama é reconhecida como a maior laguna hipersalina do mundo, cercada por dunas e vegetação de restinga que, emoldurando a sua decantada beleza natural, configura uma condição de cartão postal internacional. Isso associado à sua grande importância ecológica, faz com que ela se caracterize como um ambiente ímpar, dentro do contexto ambiental. Todavia a degradação de suas margens, ensejada pela sua ocupação desordenada, inclusive através da implantação de salinas, que vem ocorrendo há mais de um século, teve como consequência o desmatamento dessas áreas de preservação permanente, que se constituem na Faixa Marginal de Proteção (FMP). A fundamentação dessa proposta se pauta no fato de que a FMP vigente da lagoa, demarcada e aprovada através de Decreto n 42.694, de 11de novembro de 2010, não levou em conta esse aspecto de extrema relevância ambiental. Nessas condições, faz-se necessária a implementação de política voltada para ações com o objetivo de revitalizar o entorno da lagoa, de sorte a assegurar a preservação desse ecossistema localizado nas áreas limítrofes à orla da Lagoa de Araruama e garantir a sustentabilidade ambiental. O presente estudo se ateve ao levantamento das áreas em que se verificou a ocorrência de vegetação, com o intuito de ordenar a sua classificação, precipuamente com interesse em delimitar as áreas de restinga, que são consideradas Áreas de Preservação Permanente pela Resolução CONAMA 303/2002 e como parte integrante da FMP pelo Código Florestal, quando fixadoras de dunas e estabilizadoras de mangue. Em função dos resultados desse levantamento, propôs-se a inclusão, na Faixa Marginal de Proteção (FMP), das áreas em que ocorre a presença de vegetação de restinga, com respaldo no Código Florestal (Lei Federal n 4771/65) que, atualmente, disciplina o assunto, de sorte a preservar o corpo hídrico como um todo e garantir a sustentabilidade ambiental.

Biogeographic characterization of fish communities and associated benthic habitats within the Flower Garden Banks National Marine Sanctuary: sampling design and implementation of scuba surveys on the coral caps

The Flower Garden Banks National Marine Sanctuary (FGBNMS) is located in the northwestern Gulf of Mexico approximately 180 km south of Galveston, Texas. The sanctuary’s distance from shore combined with its depth (the coral caps reach to within approximately 17 m of the surface) result in limited exposure of this coral reef ecosystem to natural and human-induced impacts compared to other coral reefs of the western Atlantic. In spite of this, the sanctuary still confronts serious impacts including hurricanes events, recent outbreaks of coral disease, an increase in the frequency of coral bleaching and the massive Diadema antillarum die-off during the mid-1980s. Anthropogenic impacts include large vessel anchoring, commercial and recreational fishing, recreational scuba diving, and oil and gas related activities. The FGBNMS was designated in 1992 to help protect against some of these impacts. Basic monitoring and research efforts have been conducted on the banks since the 1970s. Early on, these efforts focused primarily on describing the benthic communities (corals, sponges) and providing qualitative characterizations of the fish community. Subsequently, more quantitative work has been conducted; however, it has been limited in spatial scope. To complement these efforts, the current study addresses the following two goals put forth by sanctuary management: 1) to develop a sampling design for monitoring benthic fish communities across the coral caps; and 2) to obtain a spatial and quantitative characterization of those communities and their associated habitats.

A point for comparison: the Flower Garden Banks National Marine Sanctuary

A reoccurring goal listed during the creation of Marine Protected Areas (MPAs) is to return the region to a former state. However, limited data is available that describes or characterizes this former condition. Data collected from ecosystems with comparatively limited anthropogenic impacts, can provide invaluable information in suggesting what former states may have looked like. One example is the Flower Garden Banks National Marine Sanctuary which is located 180 kilometers off the coast of Texas. These relatively isolated and pristine banks are capped by substantial scleractinian coral communities, forming excellent habitat for over 200 species of fish. While fishing is permitted, it is limited by difficulty of access. In 2006, NOAA’s Biogeography Branch, in collaboration with the Sanctuary, initiated the first quantitative assessment of fish resources throughout the diveable portions of the Sanctuary. The sampling design and methodologies employed were identical to those that the Branch has utilized in other more impacted regions of the US Caribbean. Initial analyses reveal that fish density and species richness at the Sanctuary were almost two times greater than that found within the US Caribbean and biomass was approximately six times higher. This was due in large part to the presence of sizeable piscivores of the genera Mycteroperca and Dermatolepis. The Sanctuary is one of few minimally impacted locations remaining within the Tropical Western Atlantic. As such, these findings should be considered when attempting to establish a former state or evaluate effectiveness of an MPA in meeting its management goals.