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The gross margin GHG emission trade-off is £0.15 kg−1 CO2 eq, representing the gross margin forgone per kg of CO2 eq reduced when GHG emissions are minimised cf. maximising farm gross margin.
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These emission factors have been considered when estimating GHG emissions from water treatment using renewable energy.
Furthermore, the Brazilian trend of novelty in all phases of sugarcane bioenergy systems should be considered when projecting GHG emissions.
When LUC GHG emissions are examined in the context of a biofuel's life cycle, they can be substantive.
In general, the level of deviation in the diets from current diets (% deviation from the current diet after normalisation by price elasticities and food expenditure shares) remained low and relatively constant when dietary GHG emissions were reduced by 40% or less.
The energy GHG emission trade-off is 0.03 GJ kg−1 CO2 eq quantifying the reduction in net energy from the farm system per kg of CO2 eq reduced when minimising GHG emissions cf. maximising net farm energy.
When minimising the GHG emissions the model will not bale the straw regardless of the price.
When minimising the GHG emissions the crop mix is 50% each of winter wheat (where 50% of the RB209 recommendation of N fertiliser is applied and the cereal straw is not baled) and winter field beans.
Similarly, JRC [10] reported very low GHG emissions when wood-derived FT diesel is produced.
The use of biofuels can result on a decrease of greenhouse gas (GHG) emissions when compared to fossil fuels.
b) Annual in-use C stocks and c) GHG emissions when half-lives set to the IPCC suggested values, (30 years for wood products).
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