The influence of fire frequency on the structure and botanical composition of savanna ecosystems

• Published in: Ecology and evolution Vol. 9; no. 14; pp. 8253 - 8264
• Main Authors: Ribeiro, Natasha, Ruecker, Gernot, Govender, Navashni, Macandza, Valério, Pais, Aurélio, Machava, Domingos, Chauque, Aniceto, Lisboa, Sa Nogueira, Bandeira, Romana
• Format: Journal Article
• Language: English
• Published: England John Wiley & Sons, Inc 01.07.2019; John Wiley and Sons Inc; Wiley
• Subjects: African Savannas; Biodiversity; Biomass; Composition; Conservation areas; Data analysis; Data collection; Density; Ecological monitoring; Ecology; Ecosystems; Environmental changes; fire ecology; Geology; Grasses; Grasslands; Herbivory; Landscape; Management; National parks; Original Research; protected areas; Random sampling; Sampling; Satellites; Savannahs; Species composition; Spectroradiometers; Statistical sampling; Studies; Trees; Vegetation; Vegetation changes; Great Limpopo Transfrontier Park; Mozambique; Africa; biodiversity; African Savannas; protected areas; fire ecology
• ISSN: 2045-7758; 2045-7758
• DOI: 10.1002/ece3.5400

Savannas cover 60% of the land surface in Southern Africa, with fires and herbivory playing a key role in their ecology. The Limpopo National Park (LNP) is a 10,000 km2 conservation area in southern Mozambique and key to protecting savannas in the region. Fire is an important factor in LNP's landscapes, but little is known about its role in the park's ecology. In this study, we explored the interaction between fire frequency (FF), landscape type, and vegetation. To assess the FF, we analyzed ten years of the Moderate resolution Imaging Spectroradiometer (MODIS) burned area product (2003–2013). A stratified random sampling approach was used to assess biodiversity across three dominant landscapes (Nwambia Sandveld‐NS, Lebombo North‐LN, and Shrubveld Mopane on Calcrete‐C) and two FF levels (low—twice or less; and high—3 times or more, during 10 years). Six ha were sampled in each stratum, except for the LN versus high FF in which low accessibility allowed only 3 ha sampling. FF was higher in NS and LN landscapes, where 25% and 34% of the area, respectively, burned more than three times in 10 years. The landscape type was the main determinant of grass composition and biomass. However, in the sandy NS biomass was higher under high FF. The three landscapes supported three different tree/shrub communities, but FF resulted in compositional variations in NS and LN. Fire frequency had no marked influence on woody structural parameters (height, density, and phytomass). We concluded that the savannas in LNP are mainly driven by landscape type (geology), but FF may impose specific modifications. We recommend a fire laissez‐faire management system for most of the park and a long‐term monitoring system of vegetation to address vegetation changes related to fire. Fire management should be coordinated with the neighboring Kruger National Park, given its long history of fire management. Synthesis: This study revealed that grass and tree/shrub density, biomass, and composition in LNP are determined by the landscape type, but FF determines some important modifications. We conclude that at the current levels FF is not dramatically affecting the savanna ecosystem in the LNP (Figure 1). However, an increase in FF may drive key ecosystem changes in grass biomass and tree/shrub species composition, height, phytomass, and density. This study revealed that grass and tree/shrub density, biomass, and composition in LNP are determined by the landscape type, but FF determines some important modifications. We conclude that at the current levels FF is not dramatically affecting the savanna ecosystem in the LNP (Figure 1). However, an increase in FF may drive key ecosystem changes in grass biomass and tree/shrub species composition, height, phytomass, and density.