28.12.2012 Views

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

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

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

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

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 />

3. Results<br />

Potential environmental impacts are provided on the Total Results and D<strong>et</strong>ailed Results she<strong>et</strong>s. Results<br />

are expressed by functional unit <strong>in</strong> six impact categories. In this study, results were for the three production<br />

systems, <strong>in</strong>clud<strong>in</strong>g the reference situation from default data and a case study for each production system (Table<br />

2), described as follows:<br />

3.1. Tomato production <strong>in</strong> a multi-tunnel greenhouse<br />

Results for the reference situation showed that the structure, fertilisers and auxiliary equipment were major<br />

contributors to all impact categories. The structure made the greatest contribution to the impact categories<br />

of abiotic depl<strong>et</strong>ion (50%), global warm<strong>in</strong>g (37%), photochemical oxidation (54%) and cumulative energy<br />

demand (50%) due to the high amount of steel and plastic <strong>in</strong> the frame, cover<strong>in</strong>g and floor. Fertilisers were<br />

the ma<strong>in</strong> burden <strong>in</strong> acidification (39%), ma<strong>in</strong>ly because of ammonia emissions <strong>in</strong>to the air dur<strong>in</strong>g their application;<br />

and eutrophication (56%), because of nitrate emissions to water, s<strong>in</strong>ce there was an open-loop irrigation<br />

system. The auxiliary equipment had significant contributions because of substrate and electricity consumption,<br />

b<strong>et</strong>ween 16% and 39%, depend<strong>in</strong>g on the impact category. The climate control system made nil<br />

contributions, as there was no heat<strong>in</strong>g. Pesticides and waste management stages made contributions below<br />

3% <strong>in</strong> the total production system.<br />

The case study for a smaller greenhouse, lower fertiliser doses and higher yield showed contributions below<br />

the reference situation, b<strong>et</strong>ween 13% and 37%, depend<strong>in</strong>g on the impact category. Structure contributions<br />

decreased b<strong>et</strong>ween 2% and 9% as the amount of m<strong>et</strong>al and plastic was reduced. Nevertheless, relative<br />

contributions of structure <strong>in</strong>creased <strong>in</strong> the total production system. Reduction of fertiliser doses directly reduced<br />

the contribution to EUP, as a lower amount of lixiviates reached aquifers. A higher yield made reductions<br />

to all impact categories, as a mass functional unit was used.<br />

3.2. Tomato production <strong>in</strong> a Venlo glass greenhouse<br />

In this production system, a CHP was used for heat<strong>in</strong>g and electricity production. Energy allocation of<br />

natural gas was used to d<strong>et</strong>erm<strong>in</strong>e the impact of us<strong>in</strong>g natural gas to heat the greenhouse (Torrellas <strong>et</strong> al.,<br />

<strong>2012</strong>). The climate control system was the ma<strong>in</strong> contributor to all the impact categories, b<strong>et</strong>ween 81% and<br />

97% of the total <strong>in</strong> the reference situation because of the high natural gas consumption to heat the greenhouse.<br />

The structure was the second burden and made contributions b<strong>et</strong>ween 2.0% and 10% because of m<strong>et</strong>al<br />

and glass contributions. Fertilisers made contributions b<strong>et</strong>ween 0.6% and 8.6% due to emissions dur<strong>in</strong>g the<br />

manufactur<strong>in</strong>g process and ammonia emissions <strong>in</strong>to the air after these fertilisers are applied to the soil. Auxiliary<br />

equipment contributions were lower than 1.9% of the total, and those of pesticides and waste management<br />

were all around 0%.<br />

With a reduction of 35% of natural gas consumption, climate control stage contributions decreased significantly<br />

<strong>in</strong> all impact categories b<strong>et</strong>ween 22% and 33%. Nevertheless, the climate control system was still<br />

the ma<strong>in</strong> burden, with contributions b<strong>et</strong>ween 75% and 95% of the total.<br />

3.3. Rose production <strong>in</strong> a Venlo glass greenhouse<br />

The climate control system was the ma<strong>in</strong> contributor <strong>in</strong> the reference situation and <strong>in</strong> this case study because<br />

of natural gas consumption for heat<strong>in</strong>g and electricity consumption for light<strong>in</strong>g. Contributions were<br />

b<strong>et</strong>ween 98% and 99% <strong>in</strong> the reference situation and the case study. The structure made contributions below<br />

1.1% <strong>in</strong> both production systems. In the case study with diffuse glass, structural contributions <strong>in</strong>creased<br />

compared with the reference situation by b<strong>et</strong>ween 4% to 16%, depend<strong>in</strong>g on the impact category, as extra<br />

electricity was needed <strong>in</strong> the anti-reflective coat<strong>in</strong>g process. In this situation, because of the effect of a higher<br />

yield, contributions to other impact categories decreased by 4% compared with the reference situation.<br />

101

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!