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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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PARALLEL SESSION 6B: FISHIERIES, SOIL, AND EMERGY METHODS 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 />

Table 4. Emergy flows and UEVs for conventional and organic oil productions. Square brack<strong>et</strong>=references<br />

for UEV; Type of <strong>in</strong>put: R= local renewable resources, N= local non-renewable resources, F= non-local<br />

purchased <strong>in</strong>puts.<br />

Emergy Fluxes (sej/ha/yr)<br />

Input Units Quantity/yr (CO) Quantity/yr (OO) Ref. UEV TYPE OF INPUT CONVENTIONAL OIL (CO) ORGANIC OIL (OO)<br />

LOCAL RESOURCES<br />

sunlight J 5,25E+13 5,25E+13 [1] R 5,25E+13 5,25E+13<br />

ra<strong>in</strong> g 7,90E+09 7,90E+09 [2] R 6,64E+14 6,64E+14<br />

geothermal heat J 3,15E+10 3,06E+10 [2] R 2,19E+14 2,13E+14<br />

loss of topsoil J 2,77E+09 2,77E+09 [3] N 2,00E+14 2,00E+14<br />

PHASE 1<br />

diesel J 3,07E+09 3,74E+10 [5] F 2,02E+14 2,46E+15<br />

fertilizer g 3,80E+05 7,40E+02 [3] F 6,23E+15 1,75E+13<br />

mach<strong>in</strong>ery g 5,23E+04 8,85E+04 [7] F 3,43E+14 5,81E+14<br />

water g 1,65E+08 1,27E+08 [8] F 2,89E+14 2,22E+14<br />

plastc, tyre g 2,43E+04 8,97E+04 [9] F 6,59E+13 2,43E+14<br />

pesticides g 9,17E+05 2,00E+04 [3] F 1,33E+16 2,90E+14<br />

electricity J 8,25E+09 6,00E+09 [4] F 9,81E+14 7,13E+14<br />

PHASE 2<br />

mach<strong>in</strong>ery g 1,54E+04 3,00E+04 [7] F 8,98E+13 1,91E+14<br />

diesel J 4,78E+08 4,78E+08 [5] F 3,14E+13 3,14E+13<br />

water g 2,27E+06 1,18E+06 [8] F 3,97E+12 2,07E+12<br />

electricity J 9,35E+08 4,84E+08 [4] F 1,11E+14 5,75E+13<br />

plastc, tyre g 4,88E+03 2,38E+04 [9] F 1,32E+13 6,45E+13<br />

glass g 6,53E+05 3,37E+05 [10] F 2,02E+15 1,04E+15<br />

HUMAN LABOUR h 8,50E+01 7,95E+02 [6] 10%R 90%F 2,51E+14 2,35E+15<br />

TOTAL 2,50E+16 9,35E+15<br />

OIL (sej/g) g 4,83E+05 2,50E+05 5,18E+10 3,74E+10<br />

OIL (sej/BOTTLE OF OIL) 5,18E+13 3,74E+13<br />

4. Discussion<br />

4.1 <strong>LCA</strong>-EME of w<strong>in</strong>e productions<br />

Literature references for UEV<br />

[1] Odum H.T., 1996.<br />

[2] Odum H.T.,<strong>et</strong> al. 2000.<br />

[3] Brandt-Williams S. L., 2002.<br />

[4] Tiezzi E. <strong>et</strong> al., 2001.<br />

[5] Bastianoni S. <strong>et</strong> al., 2009<br />

[6] Pulselli, R.M., <strong>et</strong> al., 2008.<br />

[7] Brown M.T., Bardi E., 2001.<br />

[8] Pulselli F. M.,<strong>et</strong> al., 2011.<br />

[9] Campbell D.E. <strong>et</strong> al. 2002.<br />

[10] Buranakarn, V. 1998.<br />

[11] Tilley, D.R., 1999.<br />

[12] Pulselli, R.M., <strong>et</strong> al., 2007.<br />

In w<strong>in</strong>e productions, the packag<strong>in</strong>g phase (phase 3) presents major impacts both for the production systems<br />

analysed, due to the use of glass. Impact values related to CW are higher than those of the OW (Table<br />

1) pr<strong>in</strong>cipally because the conventional system considered <strong>in</strong> this work used heavy and non-recycled glass.<br />

In contrast, the organic farm, thanks to the use of a lighter type of glass for bottles, as imposed by the European<br />

guidel<strong>in</strong>es for organic productions, can reduce impacts related to this phase. These results are <strong>in</strong> accordance<br />

with Kavargiris <strong>et</strong> al., (2009) on the organic vs. conventional w<strong>in</strong>e. Inputs l<strong>in</strong>ked to phase 1 and 2 are<br />

higher <strong>in</strong> the organic farm. CW uses chemical pesticides, effective at lower doses but with higher impact<br />

values. On the contrary, OW uses conventional sulphur and copper based pesticides, which are less effective<br />

and have to be used <strong>in</strong> higher quantities. Moreover, the CW <strong>in</strong> this study uses modern mach<strong>in</strong>eries, while <strong>in</strong><br />

the OW case most of the work is done by hand, but the mechanisation, even if highly reduced, is quite old<br />

and less efficient.<br />

EME results highlight highest values for OW’s total eMergy flow, while CW presents highest value of<br />

UEV (Table 2). It means that CW has much larger <strong>in</strong>tensive use of resources per bottle of product. This difference<br />

is due to the lower w<strong>in</strong>e productivity of CW because of the rigorous selection of grapes. OW utilises<br />

more resources than CW: less efficient mach<strong>in</strong>eries, non-synth<strong>et</strong>ic chemicals and all what concerns storage<br />

and bottl<strong>in</strong>g phase (more materials are necessary to have a higher quantity of w<strong>in</strong>e). Furthermore, the total<br />

eMergy flow is higher for the organic production pr<strong>in</strong>cipally due to the higher annual human labour and consumption<br />

of diesel per hectare. Results related to eMergy flows grouped <strong>in</strong>to macro-categories (Fig. 1) highlight<br />

how <strong>in</strong>puts are split and their weight on total eMergy flow (see the caption of Fig.1 for characteristics<br />

of each group). The category “other materials” (materials for the bottl<strong>in</strong>g phase) represents the highest percent<br />

of total eMergy flow for CW and OW respectively. While CW presents “chemical and fertilisers” as the<br />

second higher macro-category, OW presents energy contributions (diesel and electricity consumption). The<br />

slightly higher value of “human labour” <strong>in</strong> OW is because most of the work is done by hand. “Natural resources”<br />

represent less than 1% of total flows for both the two farms (not shown <strong>in</strong> the figure below).<br />

537

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