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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 1C: ECODESIGN AND ENVIRONMENTAL MANAGEMENT 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 2. Contributions to impact categories for: (2a) tomato crop <strong>in</strong> a multi-tunnel greenhouse, (2b) tomato<br />

crop <strong>in</strong> a Venlo glass greenhouse and (2c) rose crop <strong>in</strong> a Venlo glass greenhouse. Values are impact category<br />

<strong>in</strong>dicators for the reference situation (Ref) and percentage variation versus the reference situation for each<br />

case study (CS). Results are by functional unit, tonne tomato for tomato crops and 1000 stems for rose crop.<br />

2a)<br />

Auxiliary Climate control<br />

Waste<br />

Impact Total Structure equipment system Fertilisers Pesticides management<br />

category<br />

ADP,<br />

Ref C Ref C Ref C Ref Ref C Ref C Ref C<br />

kg Sb eq<br />

AAP,<br />

kg SO2<br />

1.3E+00 -14 6.4E-01 -9 4.7E-01 -19 0.0E+00 1.5E-01 -24 1.8E-02 -18 1.1E-02 3<br />

eq<br />

EUP,<br />

kg PO4<br />

9.4E-01 -18 3.3E-01 -6 2.2E-01 -18 0.0E+00 3.7E-01 -30 1.2E-02 -18 5.5E-03 5<br />

-3<br />

eq<br />

GWP,<br />

kg CO2<br />

5.0E-01 -37 1.3E-01 -2 8.3E-02 -18 0.0E+00 2.8E-01 -59 7.9E-03 -18 1.5E-03 4<br />

eq<br />

POP,<br />

kg C2H4<br />

2.0E+02 -17 7.5E+01 -6 6.2E+01 -18 0.0E+00 6.2E+01 -29 2.3E+00 -18 1.3E+00 0<br />

eq<br />

CED,<br />

3.3E-02 -13 1.7E-02 -7 1.0E-02 -18 0.0E+00 4.1E-03 -27 8.7E-04 -18 2.0E-04 4<br />

MJ 3.1E+03 -14 1.6E+03 -8 1.2E+03 -18 0.0E+00 3.0E+02 -24 4.4E+01 -18 2.5E+01 3<br />

2b) 2c)<br />

102<br />

Total Climate control system<br />

Impact categories Ref C Ref C<br />

ADP, kg Sb eq 1.5E+01 -32 1.4E+01 -33<br />

AAP, kg SO2 eq 3.3E+00 -24 2.6E+00 -29<br />

EUP, kg PO4 -3 eq 8.5E-01 -18 7.0E-01 -22<br />

GWP, kg CO2 eq 1.9E+03 -31 1.8E+03 -33<br />

POP, kg C2H4 eq 2.1E-01 -29 2.0E-01 -32<br />

CED, MJ 3.1E+04 -31 3.0E+04 -33<br />

Total Structure<br />

Impact category Ref C Ref C<br />

ADP, kg Sb eq 1.3E+01 -4 6.0E-02 11<br />

AAP, kg SO2 eq 5.9E+00 -4 5.7E-02 5<br />

EUP, kg PO4 -3 eq 3.4E+00 -4 1.8E-02 16<br />

GWP, kg CO2 eq 1.7E+03 -4 9.6E+00 8<br />

POP, kg C2H4 eq 2.6E-01 -4 2.6E-03 4<br />

CED, MJ 3.4E+04 -4 1.4E+02 14<br />

4. Discussion<br />

In this section we discuss the ma<strong>in</strong> results achieved <strong>in</strong> the study, the m<strong>et</strong>hodology used and the benefits<br />

and drawbacks of the environmental calculator. Additionally, we propose several po<strong>in</strong>ts that could be improved<br />

with future research.<br />

The ma<strong>in</strong> objective of this study was achieved with the development of an easy-to-use environmental<br />

software tool to evaluate the environmental performance of protected horticultural production systems. We<br />

consider this calculator to be a useful contribution for decision mak<strong>in</strong>g for a mix of users <strong>in</strong>volved <strong>in</strong> horticulture.<br />

<strong>LCA</strong> was appropriate to evaluate the potential impacts of protected crops objectively and transparently.<br />

The simplification of <strong>LCA</strong> <strong>in</strong> the design of this tool was done follow<strong>in</strong>g <strong>in</strong>ternational standards and guidel<strong>in</strong>es<br />

(ISO-14040, 2006 and ILCD, 2010) to justify the <strong>in</strong>clusion or exclusion of processes. As a result, the<br />

tool <strong>in</strong>cludes a justified representation of the most significant processes <strong>in</strong> a greenhouse production system.<br />

Users can easily simulate their crops and evaluate the effect on the environment of alternatives by reduc<strong>in</strong>g<br />

<strong>in</strong>puts and improv<strong>in</strong>g waste management practices. The calculator provides approximate but good quality<br />

results to compare different scenarios and follow the evolution of cleaner agricultural practices. Different<br />

damage to the environment can be studied, as six midpo<strong>in</strong>t impact categories were <strong>in</strong>cluded. The analysis of<br />

these very different structures, multi-tunnel and Venlo greenhouses, was adequately resolved by the development<br />

of specific spreadshe<strong>et</strong>s and formulas to calculate their structural materials.<br />

Simplicity is one of the ma<strong>in</strong> advantages of this calculator, but it was also the cause of some limitations.<br />

Many variables that affect agricultural systems could not be implemented <strong>in</strong> the calculator, such as geography,<br />

climate, soil characteristics, water availability and management practices such as conventional and organic<br />

farm<strong>in</strong>g. The regional variation of electricity production was not considered and consequently a more<br />

precise calculation of emissions is not possible (Torrellas, submitted). Many of these issues could be solved<br />

by <strong>in</strong>clud<strong>in</strong>g more spatial datas<strong>et</strong>s or by design<strong>in</strong>g open-source software. Fertiliser and pesticide results<br />

could be more d<strong>et</strong>ailed and pesticide toxicity could be <strong>in</strong>cluded. Therefore, the tool should be able to update<br />

the characterisation models with more recent ones such as USEtox (Rosenbaum <strong>et</strong> al., 2008) and ReCiPe<br />

(Goedkoop <strong>et</strong> al., 2009).

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