Energy DFs | ||||
---|---|---|---|---|
Authors | Country | Description | DF | Unit |
Fortin et al. (2012) | France | Domestic energy wood and industrial wood pellets replace electricity and oil | 0.076 | Mg/m3 of C eq. |
Fortin et al. (2012) | France | Wood pellets | 0.126 | Mg/m3 of C eq. |
Böttcher et al. (2012) | Germany | Substituting heating oil by biomass | 0.8 | Fossil fuel-C substituted/tonne biofuel-C harvested |
Smyth et al. (2014) | Canada | Domestic bioenergy | −0.08–0. 79 | Mg C/Mg C |
Smyth et al. (2014) | Canada | International bioenergy | 0.6 | Mg C/Mg C |
Knauf et al. (2015) | Germany | Fuel substitution | 0.67 | t C/t C |
Soimakallio et al. (2016) | Finland | Substitution factor for paper products (fossil fuel substitution) | 0.8 | t C/t C |
Soimakallio et al. (2016) | Finland | Substitution factor for paperboard products (plastics, fossil fuel substitution) | 1.40 | t C/t C |
Soimakallio et al. (2016) | Finland | Substitution factor for energy and post-used mechanical wood products (fossil fuel substitution) | 0.47–0.89 | t C/t C |
Knauf (2016) | Germany | Fuel substitution | 0.67 | t C/t C |
Knauf et al. (2016) | Germany | Fuel substitution | 0.67 | t C/t C |
Han et al. (2016) | South Korea | Sawnwood and industrial roundwood substituting fossil fuels for heating purposes | 0.076 | Mg/m3 C eq. |
Han et al. (2016) | South Korea | Wood pellets and industrial roundwood substituting fossil fuels for heating purposes | 0.126 | Mg/m3 C eq. |
Matsumoto et al. (2016) | Japan | Logging residues, process residues and waste wood; Substitution of residues and waste wood for heavy oil kg | 108.9 | kg C/m3 |
Cintas et al. (2016) | Sweden | Forest-based bioenergy | 0.55–1.27 | Mg of fossil C is displaced/Mg of C in biomass used |
Smyth et al. (2017a) | Canada | Bioenergy from harvest residues | 0–2 | t C/t C |
Härtl et al. (2017) | Germany | Timber used in energy production | 0.67 | t Cfossil/t Ctimber |
Smyth et al. (2017b) | Canada | Bioenergy using an optimized selection of bioenergy facilities which maximized avoided emissions from fossil fuels. | 0.47–0.89 | t C/t C |
Ji et al. (2016) | China | Substitute for Coal | 0.96 | t C/t C |
Ji et al. (2016) | China | Substitute for Oil | 0.79 | t C/t C |
Ji et al. (2016) | China | Substitute for Natural Gas | 0.56 | t C/t C |
Baul et al. (2017) | Finland | Energy biomass | 0.5 | t C/t C |
Suter et al. (2017) | Switzerland | Heat replacing light fuel oil | 0.55 | t CO2-eq/m3 |
Suter et al. (2017) | Switzerland | Heat replacing natural gas | 0.32 | t CO2-eq/m3 |
Suter et al. (2017) | Switzerland | Electricity mix CH | 0.12 | t CO2-eq/m3 wood |
Schweinle et al. (2018) | Germany | Displacement of fossil fuel with wood fuel | 0.67 | t C/t C |
Chen et al. (2018) | Canada | Wood used to produce energy for the HWP industry reduced fossil fuel-based emissions | 2.00 | t CO2 eq/t C in wood |
Smyth et al. (2018) | Canada | Collected harvest residues for bioenergy, energy demand and displacement factors two forest management unit | 0.38, 0.95 | t C/t C |
Köhl et al. (2020) | Germany | Lignite substitution in order to achieve carbon neutrality | 1.9 | t C/t C |
Köhl et al. (2020) | Germany | Gas substitution in order to achieve carbon neutrality | 2.5 | t C/t C |
Hurmekoski et al. (2020) | Finland | Wood use replacing CHP of fossil origin | 0.7 | t C/t C |
Hurmekoski et al. (2020) | Finland | Wood-based transport fuel replacing diesel | 0.63 | t C/t C |
Hurmekoski et al. (2020) | Finland | Wood-based ethanol replacing transport fuel | 0.7 | t C/t C |