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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 3B: PACKAGING 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 />

sidered as be<strong>in</strong>g at the boundary of this system as the recovered material has no changes <strong>in</strong> its <strong>in</strong>herent properties.<br />

The paraff<strong>in</strong> obta<strong>in</strong>ed is used to replace the p<strong>et</strong>rochemical naphtha that is a precursor of poly<strong>et</strong>hylene<br />

production. This reverse flow was called “recycled poly<strong>et</strong>hylene” and was applied to discount the use of<br />

virg<strong>in</strong> poly<strong>et</strong>hylene. Fig. 1 shows the boundaries of the system evaluated, along with the recycl<strong>in</strong>g model<br />

used. This m<strong>et</strong>hod was used for modell<strong>in</strong>g the system <strong>in</strong> 2000 with no recycl<strong>in</strong>g and the system <strong>in</strong> 2011 for<br />

recycl<strong>in</strong>g rates of 0%, 27%, 35%, 50% and 70%.<br />

T<br />

Forestry (wood<br />

production)<br />

Cellulose<br />

production<br />

Cardboard<br />

manufactur<strong>in</strong>g<br />

Cellulose virg<strong>in</strong> kg<br />

T<br />

Cardboard<br />

Aseptic lam<strong>in</strong>ate production with x % recycl<strong>in</strong>g<br />

Milk consumption<br />

Post-consumer packag<strong>in</strong>g recycl<strong>in</strong>g:<br />

cellulose fibers (Rc kg)<br />

PE/Al residue (PEAl kg)<br />

Paraff<strong>in</strong> (P kg) and alum<strong>in</strong>um (Al<br />

plasma kg) recovered by plasma<br />

Oil extraction<br />

P<strong>et</strong>rochemical<br />

naphtha<br />

(N- P) kg<br />

Ethylene<br />

production<br />

Poly<strong>et</strong>hylene<br />

Milk fill<strong>in</strong>g (1,000 litres)<br />

Figure 1. Model used to account the production and recover<strong>in</strong>g of the aseptic milk packag<strong>in</strong>g (open-loop<br />

with closed-loop recycl<strong>in</strong>g procedure and expanded system boundaries).<br />

2.4 Environmental impact categories evaluated<br />

T<br />

Recovered<br />

cellulose fibres<br />

(Rc kg)<br />

PEAl for plasma<br />

kg<br />

T<br />

T<br />

Paraff<strong>in</strong> (P kg)<br />

Recycled<br />

<strong>et</strong>hylene<br />

production<br />

Recycled<br />

poly<strong>et</strong>hylene<br />

T T T<br />

R% – recycl<strong>in</strong>g rate<br />

PE/Al roof tiles<br />

production (Rt kg)<br />

Bauxite m<strong>in</strong><strong>in</strong>g<br />

Alum<strong>in</strong>a<br />

production<br />

Primary<br />

alum<strong>in</strong>um<br />

production<br />

Alum<strong>in</strong>um foil<br />

F<strong>in</strong>al disposal<br />

<strong>in</strong> landfills<br />

The <strong>in</strong>ventories obta<strong>in</strong>ed were evaluated accord<strong>in</strong>g to the CML 2001 m<strong>et</strong>hodology developed by the Center<br />

of Environmental Science at Leiden University (Gu<strong>in</strong>née <strong>et</strong> al., 2001) and updated <strong>in</strong> December, 2007 for the<br />

follow<strong>in</strong>g environmental impact categories and <strong>in</strong> accordance with the pr<strong>in</strong>ciples of ISO Standard 14044:<br />

abiotic depl<strong>et</strong>ion potential – ADP (kg Sb equiv), global warm<strong>in</strong>g potential – GWP (kg CO2 equiv.), acidifica-<br />

T<br />

PEAl kg – PEAl for plasma<br />

kg<br />

T<br />

Emissions<br />

Inverse process of virg<strong>in</strong> alum<strong>in</strong>um<br />

production:<br />

(Al tile equivalent to Rt kg)<br />

Resources<br />

T<br />

Al virg<strong>in</strong> kg<br />

Al plasma kg<br />

T<br />

Milk production<br />

and sterilization<br />

Emissions<br />

from milk<br />

consumption<br />

Milk<br />

277

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