Abstract :
[en] Wetlands provide essential ecosystem services in Africa, yet their extent and fragmentation remain poorly understood. Here we classify African wetlands at 10 m resolution, using seasonal composite imagery and a random forest algorithm. We estimate a total wetland area of 947,750 km² (10% of global wetlands), comprising 46% marshes, 25% swamps, 22% peatlands, 5% seasonal wetlands, and 2% mangroves. Wetland fragmentation is strongly associated with high population densities in countries such as Nigeria, Liberia, Guinea, Egypt, Algeria, and Kenya. African wetlands store an estimated 54 ± 11 Gt of carbon, surpassing Europe's 12-31 Gt. If drained, they could release 260 MtC yr − ¹, nearly ten times the carbon sequestration of pristine wetlands (27 MtC yr − ¹). These findings provide a crucial foundation for sustainable wetland management and policy development. African wetlands are among the most productive ecosystems in the world 1 , providing a wide range of services that contribute to human wellbeing, such as the provision of water, food, dry season grazing, and fuel wood. They can support a wide range of flora and fauna and serve as an important carbon pool, sequestrating large amounts of carbon from the atmosphere, thereby regulating climate 2. Depending on topographic context, wetlands can also play a significant function in flood attenuation and shoreline protection 3-5 and also play a key role in the hydrological cycle 6. Wetlands are dynamic ecosystems that can be categorized based on their hydrology, soil composition, and vegetation types, each supporting unique ecological functions and biodiversity. Marshes, for instance, are wetlands dominated by herbaceous (non-woody) plants, characterized by periodic or continuous flooding. They can be found in both freshwater and saline environments, where nutrient-rich soils foster diverse flora and fauna. Swamps are wetlands with mineral soils (although some classifications also distinguish organic soil peat swamps), dominated by woody vegetation such as trees and shrubs. These ecosystems experience seasonal or permanent flooding and include coastal mangrove swamps, which are crucial for coastal protection, carbon sequestration, and biodiversity conservation. Peatlands represent a distinct wetland category, defined by the accumulation of partially decomposed organic matter (peat) due to water saturation. Peatlands are further classified into bogs and fens. Bogs are rain-fed (ombrotrophic) systems that are typically acidic and nutrient-poor, often supporting mosses, shrubs, and sometimes trees. Fens, by contrast, are groundwater-fed (minerotrophic) and more nutrient-rich, allowing for a mix of grasses, sedges, and woody vegetation. Seasonal wetlands, another important type, experience periodic inundation during specific times of the year, followed by dry conditions. These include natural systems like ephemeral ponds and human-made systems such as rice paddies, which harbor species adapted to fluctuating water levels. Amongst these wetland types, marshes are especially susceptible to anthropogenic pressures because of their accessibility, fertile soils, and proximity to densely populated regions. High demand for agricultural and urban development, combined with inadequate protection measures, makes these wetlands highly vulnerable and often heavily exploited. In this study, wetlands are broadly classified into five types: swamps (mineral soil dominated), marshes including seasonal marshes are classified under the broader category of marshes, emphasizing vegetation type as the primary distinguishing factor, peatlands
Funding text :
This projectwas funded by a studentship awarded to SIG (PTDF/ED/PHD/
1301/17) under the Petroleum Technology and Development Fund
(PTDF), Nigeria. The photo-interpretation dataset was part of the global
dryland assessment, whichwas conducted in the region by the Food and
Agriculture Organization and the National Space Research and Development
Agency of Nigeria. Ground control data points for some peatlands
in East Africa were extracted from the Global Peatland Database
(GPD) collated by Greifswald Mire Center and we specifically acknowledge
support from Alexandra Barthelmes. S.K.E. is supported by a NERC
Independent Research Fellowship (NE/R015546/1) and is a member of
the NERC-BGS Center for theObservation andModeling of Earthquakes,
Volcanoes, and Tectonics (COMET).
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