The Center for International Forestry Research (CIFOR and World Agroforestry (ICRAF) joined forces in 2019, leveraging a combined 65 years’ experience in research on the role of forests and trees in solving critical global challenges.
Year
2021
Authors
Aynekulu EAynekulu E
, Sileshi G WSileshi G W
, Rosenstock T SRosenstock T S
, van Noordwijk Mvan Noordwijk M
, Tsegaye D, Koala J, Sawadogo L, Milne E, De Leeuw JDe Leeuw J
, Shepherd K DShepherd K D
Ermias Betemariam is a land health scientist with research interest in land degr...
Sileshi obtained a BSc degree in Biology in 1987, MSc degree in Agriculture in 1...
Todd Rosenstock is an agroecologist with the World Agroforestry (ICRAF) where he...
Meine van Noordwijk is a Distinguished Research Fellow at World Agroforestry. He...
Jan de Leeuw is Senior Scientist Drylands Systems at World Agroforest...
Keith Shepherd’s research focuses on land health surveillance – an evidence-base...
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Fire and overgrazing reduce aboveground biomass, leading to land degradation and potential impacts on soil organic carbon (SOC) and total nitrogen (TN) dynamics. However, empirical data are lacking on how prescribed burning and livestock exclusion impact SOC in the long-term. Here we analyse the effects of 19 years of prescribed annual burning and livestock exclusion on tree density, SOC and TN concentrations in the Sudanian savanna ecoregion at two sites (Tiogo and Laba) in Burkina Faso. Results revealed that neither livestock exclusion nor prescribed burning had significant impact on SOC and TN concentrations. The results at both sites indicate that 19 years of livestock and fire exclusion did not result in a significant increase in tree density compared to grazing and annual prescribed burning. The overall mean (± SEM) of SOC stocks in the 0–50 cm depth increment in the unburnt (53.5 ± 4.7 Mg C ha−1) and annually burnt (56.4 ± 4.3 Mg C ha−1) plots at Tiogo were not statistically different. Similarly, at Laba there was no significant difference between the corresponding figures in the unburnt (37.9 ± 2.6 Mg ha−1) and in the annually burnt plots (38.6 ± 1.9 Mg ha−1). Increases in belowground inputs from root turnover may have countered changes in aboveground biomass, resulting in no net change in SOC and TN. We conclude that, contrary to our expectation and current policy recommendations, restricting burning or grazing did not result in increase in SOC stocks in this dry savanna ecosystem.





