Abstract

Mangrove forests have experienced a rapid decline. However, the rate of loss has decreased in recent years due to enhanced conservation and nature regeneration. The dynamics of mangrove forests in Panama have not been monitored since the year 2000, despite a significant loss during the 1980s. The objectives of our study were to quantify changes in mangrove cover and identify the dominant drivers of change in Parita Bay, Panama. Temporal changes in mangrove cover and the Normalized Difference Vegetation Index (NDVI) were determined using the supervised classification method on Landsat satellite images from 1987 to 2019. We identified a 4.7% increase in the mangrove area of Parita Bay during the 32 years; the mangrove forests were also considered healthy as reflected by high NDVI values. However, the conversion of mangroves to other land cover types resulted in a 1.26% decline in mangrove cover from 1987 to 1998. Moreover, the area of aquaculture and saltpans almost doubled during this period. During the following two decades, the conversion of other land cover classes (water, other vegetation, and bare soil) increased the mangrove area by 6%, and the annual rate of increase was greater during the second decade (0.43% year−1). From 2009 to 2019, mangroves declined at an annual rate of 0.11% in protected areas and increased at an annual rate of 0.50% in unprotected areas. Despite the regeneration potential of mangrove forests, our study highlights the need to continually manage and protect mangrove forests in order to facilitate their expansion in Parita Bay.

Highlights

  • Mangroves comprises the group of halophytic trees, shrubs and plants positioned in the critical interface between terrestrial, estuarine, and near-shore marine ecosystems in the tropical and subtropical coastlines

  • It can be said that most errors in the mangrove cover classification fall upon the Producer rather than the User; in other words, mangrove class tends to be underestimated in the map

  • In the map, it is classified as bare soil class, but in the field, it seems as mangroves regenerating, it is identified as mangrove class, generating errors of omission

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Summary

Introduction

Mangroves comprises the group of halophytic trees, shrubs and plants positioned in the critical interface between terrestrial, estuarine, and near-shore marine ecosystems in the tropical and subtropical coastlines There are many studies highlighting the importance of mangrove forest due to the ecosystem services they provide, such as nurseries for marine species, sediment stabilization, water purification, woody and nonwoody forest products, conservation of biological diversity, coastal protection, and highest rate of carbon sequestration (Friess, 2016; Godoy, De Andrade Meireles, & De Lacerda, 2018; Rioja-Nieto, Barrera-Falcón, Torres-Irineo, Mendoza-González, & Cuervo-Robayo, 2017). As one of the most effective carbon sink forests, mangrove can contain an average of 937 tC ha-1, promoting speedy rates of sediment deposit (~5 mm year-1) and carbon burial (174 gC m2 year-1) (Alongi, 2012). Mangroves forest and its soils can sequester approximately 22.8 million metric tons of carbon each year worldwide (Giri et al, 2011)

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