Abstract

AbstractSeveral EU countries import wood pellets from the south‐eastern United States. The imported wood pellets are (co‐)fired in power plants with the aim of reducing overall greenhouse gas (GHG) emissions from electricity and meeting EU renewable energy targets. To assess whether GHG emissions are reduced and on what timescale, we construct the GHG balance of wood‐pellet electricity. This GHG balance consists of supply chain and combustion GHG emissions, carbon sequestration during biomass growth and avoided GHG emissions through replacing fossil electricity. We investigate wood pellets from four softwood feedstock types: small roundwood, commercial thinnings, harvest residues and mill residues. Per feedstock, the GHG balance of wood‐pellet electricity is compared against those of alternative scenarios. Alternative scenarios are combinations of alternative fates of the feedstock materials, such as in‐forest decomposition, or the production of paper or wood panels like oriented strand board (OSB). Alternative scenario composition depends on feedstock type and local demand for this feedstock. Results indicate that the GHG balance of wood‐pellet electricity equals that of alternative scenarios within 0–21 years (the GHG parity time), after which wood‐pellet electricity has sustained climate benefits. Parity times increase by a maximum of 12 years when varying key variables (emissions associated with paper and panels, soil carbon increase via feedstock decomposition, wood‐pellet electricity supply chain emissions) within maximum plausible ranges. Using commercial thinnings, harvest residues or mill residues as feedstock leads to the shortest GHG parity times (0–6 years) and fastest GHG benefits from wood‐pellet electricity. We find shorter GHG parity times than previous studies, for we use a novel approach that differentiates feedstocks and considers alternative scenarios based on (combinations of) alternative feedstock fates, rather than on alternative land uses. This novel approach is relevant for bioenergy derived from low‐value feedstocks.

Highlights

  • The EU aims to increase the share of renewable energy in its gross final energy consumption to 20% by the year 2020 to mitigate climate change and improve energy security of supply (EU directive 2009/28/EC)

  • Our results show how the greenhouse gas (GHG) balances of wood-pellet electricity from different feedstocks compare to the GHG balances of individual counterfactuals (Fig. 3) and of alternative scenarios (Fig. 4)

  • The GHG balance of wood-pellet electricity from all feedstocks is positive, because the avoided fossil electricity emissions are higher than net emissions from wood-pellet electricity itself

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Summary

Introduction

The EU aims to increase the share of renewable energy in its gross final energy consumption to 20% by the year 2020 to mitigate climate change and improve energy security of supply (EU directive 2009/28/EC). A type of solid biofuel, form one such renewable and accounted for 0.47% of EU gross inland energy consumption in 2014 (Aebiom, 2015; Eurostat, 2016). SE go to the EU (Pinchot institute, 2013; Abt et al, 2014; EIA, 2014). Driven by EU demand (Abt et al, 2014), US SE wood-pellet production and export have doubled since 2011 (Eurostat, 2015; Prestemon et al, 2015), making the region one of the largest global wood-pellet suppliers to the EU (Hoefnagels et al, 2014). The wood-pellet market is small relative to that of other forest products (e.g. saw timber or paper), with wood pellets having comprised

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