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LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

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GROUP 4, SESSION B: CROP PRODUCTION SYSTEMS 8 th Int. Conference on <strong>LCA</strong> <strong>in</strong> the<br />

Agri-<strong>Food</strong> Sector, 1-4 Oct <strong>2012</strong><br />

806<br />

100. Environmental implications of us<strong>in</strong>g biomass versus fossil fuels<br />

for energy production: the case of willow, an energy crop<br />

Thu Lan T. Nguyen * , John E. Hermansen<br />

Dept. of Agroecology, Aarhus University, Blichers Allé 20, Postbox 50, DK-8830 Tjele, Denmark, Correspond<strong>in</strong>g<br />

author. E-mail: ThuLan.ThiNguyen@agrsci.dk<br />

Fossil fuel use for energy production is fac<strong>in</strong>g serious problems related to resource depl<strong>et</strong>ion and environmental<br />

degradation, notably climate change. Biomass fuels e.g. wood waste, crop residues, energy crops, <strong>in</strong><br />

contrast, are considered renewable and carbon neutral. Unlike fossil fuels that take millions of years to be<br />

available as an energy source, biomass can be regenerated relatively quickly through photosynthesis. Biomass<br />

burn<strong>in</strong>g releases CO2 back to the atmosphere but this biogenic CO2 is not counted as contribut<strong>in</strong>g to<br />

global warm<strong>in</strong>g. Apart from wood waste and crop residues, energy crops e.g. willow and miscanthus have<br />

recently received large attention as a potential source of renewable energy. Whereas biomass is “carbon neutral”<br />

when burned, the <strong>in</strong>puts used to produce it may be a source of CO2 and other GHG emissions.<br />

Our research questions were: (1) What if the upstream impacts of energy production from biomass fuels, i.e.<br />

those connected with biomass cultivation and distribution, are <strong>in</strong>cluded?, (2) In addition to global warm<strong>in</strong>g<br />

and non-renewable energy, what about other impact categories like acidification, eutrophication, ecotoxicity,<br />

human toxicity, <strong>et</strong>c., and 3) How to account for trade-offs among different impact categories? A thorough<br />

and comprehensive analysis is thus necessary to assess the susta<strong>in</strong>ability of substitut<strong>in</strong>g biomass for fossil<br />

fuels <strong>in</strong> energy production. The task is not only to <strong>in</strong>clude more impact categories than global warm<strong>in</strong>g and<br />

non-renewable energy but also to perform the analysis at a more aggregated level, i.e., translat<strong>in</strong>g impacts <strong>in</strong><br />

different mid-po<strong>in</strong>t categories <strong>in</strong>to a s<strong>in</strong>gle unit so that they can be weighted and added tog<strong>et</strong>her to give a<br />

s<strong>in</strong>gle score value.<br />

In this paper, we present as a case study the results of an <strong>LCA</strong> study on electricity generation from willow<br />

produced on arable land, <strong>in</strong> comparison with fossil fuels. Inventory data for the entire process from willow<br />

cultivation to energy production were from Nielsen and Illerup (2003) and Uellendahl <strong>et</strong> al. (2008). Midpo<strong>in</strong>t<br />

impact categories considered were global warm<strong>in</strong>g, non-renewable energy, acidification, eutrophication,<br />

respiratory <strong>in</strong>organics, human toxicity, ecotoxicity, photochemical ozone and nature occupation. All midpo<strong>in</strong>t<br />

impacts were then translated <strong>in</strong>to a s<strong>in</strong>gle mon<strong>et</strong>ary unit. The LCIA m<strong>et</strong>hod used was Stepwise 2006<br />

(Weidema, 2009). For a verification of the mon<strong>et</strong>arisation scheme used <strong>in</strong> the Stepwise2006 m<strong>et</strong>hod versus<br />

that used <strong>in</strong> previous studies, a sensitivity analysis was also performed.<br />

The midpo<strong>in</strong>t impact assessment shows that substitution of willow for fossil fuels would br<strong>in</strong>g both environmental<br />

benefits and costs. The substitution for coal offered environmental benefits <strong>in</strong> all impact categories<br />

considered except for nature occupation and eutrophication. The substitution for natural gas reduced<br />

impacts on human toxicity, ecotoxicity, global warm<strong>in</strong>g and non-renewable energy but <strong>in</strong>creased nature occupation,<br />

eutrophication, respiratory <strong>in</strong>organics, acidification and photochemical ozone. The results at the<br />

aggregated level show that energy production from willow scores b<strong>et</strong>ter than from coal (0.11 vs. 0.12<br />

EUR/kWh) but worse than from natural gas (0.11 vs. 0.06 EUR/kWh). Much of this <strong>in</strong>ferior performance is<br />

accounted for by the impact on nature occupation of biomass fuel crops; nature occupation is by far the ma<strong>in</strong><br />

contributor with a share of approx. 80% of the aggregated s<strong>in</strong>gle score. Nature occupation thus rema<strong>in</strong>s a<br />

major environmental hotspot for bioenergy development, stress<strong>in</strong>g the importance of seek<strong>in</strong>g improvements<br />

<strong>in</strong> relation to this <strong>in</strong>dicator <strong>in</strong> order for biomass fuels like energy crops to be a viable fuel source.<br />

References<br />

Nielsen, M., Illerup, J.B., 2003. Emissionsfaktorer og emissionsopgørelse for decentral kraftvarme, Eltra<br />

PSO projekt 3141, Kortlægn<strong>in</strong>g af emissionsfaktorer fra decentral kraftvarme, Delrapport 6, Faglig rapport<br />

fra DMU, nr. 442.<br />

Uellendahl, H., Wang, G., Moller, H.B. <strong>et</strong> al., 2008. Energy balance and cost-benefit analysis of biogas production<br />

from perennial energy crops pre-treated by w<strong>et</strong> oxidation. Water Sci Technol. 58, 1841-1847<br />

Weidema, B.P., 2009. Us<strong>in</strong>g the budg<strong>et</strong> constra<strong>in</strong>t to mon<strong>et</strong>arise impact assessment results. Ecological Economics<br />

68, 1591-1598.

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