Life Cycle Assessment of biodiesel using jatropha as feedstock

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Life Cycle Assessment of biodiesel using jatropha as feedstock under the frame of the JatroMed project implementation Elena Koukouna Lignocellulosic Crops as feedstock for future Biorefineries Summer School 26-31 July 2014, Lisbon

Outline Introduction Goal of Study Methods Impact Results Conclusions Recommendations

Introduction JatroMed (www.jatromed.aua.gr), is a 4-year demonstration project, coordinated by the Agricultural University of Athens, Greece and co-financed by European Union. The programme is focusing on the cultivation of energy crop Jatropha curcas L. in small-scale, community-based initiatives for local uses in Morocco, Algeria and Egypt. Case study used for thesis project; Essaouira, Morocco

Morocco Essaouira Region: commune Hadd Dra - 31 34 39.56 N, 09 32 19.45 W Poverty Rate Less than 5% Above 30% Hadd Dra

Goal of the study Main goal Comprehensive LCA of jatropha biodiesel (proper data bookkeeping, evaluation of methodological choices) Main Objective: comparative analysis - of biodiesel system performance and the equivalent petroleum diesel system; - of the cultivation treatments used within JatroMed (Michoacan and JCLMax)

Goal of the study Main goal Comprehensive LCA of jatropha biodiesel (proper data bookkeeping, evaluation of methodological choices) Main Objective: comparative analysis - of biodiesel system performance and the equivalent petroleum diesel system; - of the cultivation treatments used within JatroMed (Michoacan and JCLMax)

Introduction Definition Life Cycle Assessment (LCA) is an analytical method that measures the energy and resource inputs and corresponding environmental releases of a product (good, or service) and evaluates its environmental performance.

Jatropha biodiesel Life Cycle CULTIVATION emissions EXTRACTION CO2 CO2 biogenic emissions ENERGY & MATERIAL INPUT BY-PRODUCTS WASTE REFINING TRANSPORTATION FUEL BIODIESEL CONVERSION ALCOHOL

Methodology Methods The model was constructed in CMLCA software of Leiden University, NL The LCA adheres to the principles, framework and guidelines in ISO-14000 series standard Inventory data collection JatroMed demonstration fields (nurseries & cultivation) Ecoinvent database Literature review Interviews

Methodology Product system properties Functional unit; 1km of driving a lorry running on diesel System boundaries are set from cradle to grave Allocation is based on both economic and energy flows TREATMENT A1: Fertilization 10 g of urea per plant Every month both doses will be increased by 5 g TREATMENT B2: Irrigation 8L/hour every 7 days Reference scenario A1B2 Low fertilization/ High irrigation (170 kg Urea/ha.yr, 900 m 3 irrig.water/ ha.yr) 3500 kg DM seed yield/ ha.yr (basic assumption) 20 years lifetime

System Boundaries of jatropha biodiesel System boundaries set for the study Cradle to Grave

Preliminary Impact Results 7,00E-14 Conventional VS Alternative system Normalized Impact Results - Energy Allocation 6,00E-14 5,00E-14 4,00E-14 3,00E-14 2,00E-14 1,00E-14 jatropha biodiesel lorry petroleum diesel lorry 0,00E+00

Preliminary Impact Results Conventional VS Alternative 7,00E-14 Conventional VS Alternative system Normalized Impact Results - Energy Allocation 6,00E-14 5,00E-14 4,00E-14 3,00E-14 2,00E-14 1,00E-14 jatropha biodiesel lorry petroleum diesel lorry 0,00E+00

Preliminary Impact Results Conventional VS Alternative 7,00E-14 Conventional VS Alternative system Normalized Impact Results - Energy Allocation 6,00E-14 5,00E-14 4,00E-14 3,00E-14 2,00E-14 1,00E-14 jatropha biodiesel lorry petroleum diesel lorry 0,00E+00

Major contributors of Impact Categories 60% 50% 40% 30% 20% 10% Major contributors of GWP along jatropha biodiesel life cycle (%) use phase energy consumption (combustion of foss.fuels) industrial waste transport mining (minerals, metals) fertilizer production 0% -10% GWP100 materials and chemicals use fossil resource extraction -20% cultivation -30% -40% application of jatropha residues to the crops others -50%

120 Major contributors of Acidification along jatropha biodiesel life cycle (%) 100 use phase 80 energy production consumption (foss. fuels) 60 40 bulding machines use (fuel combustion) transport others 20 0 Acidification

120 Major contributors of Eutrophication along jatropha biodiesel life cycle (%) 100 80 anaerobic digestion (j.residues) use phase 60 40 energy production (combustion of hard coal) building machines use (fuel combustion) transport 20 others 0 Eutrophication

Eutrophication scenarios 0,0035 Eutrophication (kg PO4 eq.) 0,003 0,0025 0,002 0,0015 Eutrophication 0,001 0,0005 0 Reference system No fertilization no j.residues application petroleum diesel

Delivering 1km driving on jatropha biodiesel Land use change; 0.142 m2.yr land - Almost entirely due to occupation of arable land - Occupation of industrial land Land use change due to C-stock change; -1.3 tn CO2 / ha.yr (IPCC methodology) Water footprint; 0.116 m3 water Energy consumption; 7.83 MJ (fossil based) Oil demand; 0.336 kg crude j.oil or 0.271 kg j.biodiesel 1km

Conclusions GWP for petroleum diesel system is 5 times larger than biodiesel, while acidification and eutrophication are lower by 35% and 70% respectively. For biodiesel system, negative global warming emissions are due to CO2 fixation (distinction btw short and long life carbon) By-products treatment may considerably affect the life cycle emissions

Recommendations for further research Agronomic practices (soil quality improvement, water use enhancement, crop residue and fertilizer management) Nutrient cycling by using by-products Possibilities of intercropping Energy consumption in agricultural, refining and manufacturing processes Biodiesel conversion technologies (processing conditions, catalysts use)

Thank you for your attention Acknowledgement The data used in this work was taken from the EU funded project JatroMed (www.jatromed.aua.gr) This work was supported by the European Union These supports are gratefully appreciated Lignocellulosic Crops as feedstock for future Biorefineries, Summer School 26-31 July 2014, Lisbon

Major contributors per impact Abiotic depletion: - Mining - Extraction of fossil fuels GWP: - Use phase (highest contributor) - Energy production (fossil) - Industrial waste - Mining of heavy metals - Fertilizer production Human toxicity: - Intensive materials production; Steel production 25% & Copper production 13% category Terrestrial ecotoxicity: - Materials production ~65% Acidification: - Use phase 55% - Energy production - Transport Eutrophication: - Application of jatropha residues 62% (mineral nutrient overenrichment) - Use phase 28%