Abstract

AbstractSmall‐scale Jatropha cultivation and biodiesel production have the potential of contributing to local development, energy security, and greenhouse gas (GHG) mitigation. In recent years however, the GHG mitigation potential of biofuel crops is heavily disputed due to the occurrence of a carbon debt, caused by CO2 emissions from biomass and soil after land‐use change (LUC). Most published carbon footprint studies of Jatropha report modeled results based on a very limited database. In particular, little empirical data exist on the effects of Jatropha on biomass and soil C stocks. In this study, we used field data to quantify these C pools in three land uses in Mali, that is, Jatropha plantations, annual cropland, and fallow land, to estimate both the Jatropha C debt and its C sequestration potential. Four‐year‐old Jatropha plantations hold on average 2.3 Mg C ha−1 in their above‐ and belowground woody biomass, which is considerably lower compared to results from other regions. This can be explained by the adverse growing conditions and poor local management. No significant soil organic carbon (SOC) sequestration could be demonstrated after 4 years of cultivation. While the conversion of cropland to Jatropha does not entail significant C losses, the replacement of fallow land results in an average C debt of 34.7 Mg C ha−1, mainly caused by biomass removal (73%). Retaining native savannah woodland trees on the field during LUC and improved crop management focusing on SOC conservation can play an important role in reducing Jatropha's C debt. Although planting Jatropha on degraded, carbon‐poor cropland results in a limited C debt, the low biomass production, and seed yield attained on these lands reduce Jatropha's potential to sequester C and replace fossil fuels. Therefore, future research should mainly focus on increasing Jatropha's crop productivity in these degraded lands.

Highlights

  • The current demand for reducing greenhouse gas (GHG) emissions, in combination with the depletion of fossil fuel reserves and the growing concern on energy security and independence (Verrastro & Ladislaw, 2007) led to a growing interest in the production of liquid biofuels

  • Unlike many previous repayment time studies, this study is completely based on field data, which means that the analysis takes into account local specificities which can strongly influence the results and are often missed by modeling approaches

  • Our C stock data can serve as valuable input for local Jatropha biofuel policy (Witcover et al, 2013), Jatropha sustainability and C sequestration assessments and for estimating benefits from selling Jatropha-based C credits

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Summary

Introduction

The current demand for reducing greenhouse gas (GHG) emissions, in combination with the depletion of fossil fuel reserves and the growing concern on energy security and independence (Verrastro & Ladislaw, 2007) led to a growing interest in the production of liquid biofuels. 2014) and a large fraction of Jatropha initiatives failed because of low yields due to insufficient agronomic knowledge (Nielsen et al, 2013; Singh et al, 2014) Despite this negative experience, small-scale Jatropha cultivation can still play an important role as a local energy source in low-income areas (e.g., Sahel region), thereby contributing to local development, energy security, and GHG mitigation (Achten et al, 2010b; Nielsen et al, 2013; Muys et al, 2014). Besides the well-known environmental benefits, GHG mitigation can boost the economic viability of Jatropha projects through C trading mechanisms (Nielsen et al, 2013; Van Rooijen, 2014)

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