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 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 />

The sensitivity analysis showed that the environmental impacts could <strong>in</strong>crease from 2% (GWP) up to 5%<br />

(AP) if the credits were disregarded.<br />

4. Discussion<br />

The closed-loop recycl<strong>in</strong>g procedure tog<strong>et</strong>her with the expansion of system boundaries were used <strong>in</strong> order to<br />

account for all the valuable products from this cha<strong>in</strong>. The model used represents the real situation concern<strong>in</strong>g<br />

the production of roof tiles, recovered cellulose fibres, and also alum<strong>in</strong>ium and paraff<strong>in</strong> recovered by plasma<br />

technology. There are some uncerta<strong>in</strong>ties related to the credit of alum<strong>in</strong>ium due to the production of roof<br />

tiles and the paraff<strong>in</strong> substitution of the p<strong>et</strong>rochemical naphtha.<br />

The alum<strong>in</strong>ium credit is not totally correct because the ma<strong>in</strong> comp<strong>et</strong>itor of post-consumer roof tile is cement<br />

tile and not alum<strong>in</strong>ium tile (the only <strong>in</strong>ventory available). Paraff<strong>in</strong> is not a p<strong>et</strong>rochemical naphta, but this<br />

approach is a way to account for the reduction <strong>in</strong> the oil required for <strong>et</strong>hylene production.<br />

The sensitivity analysis showed that recycl<strong>in</strong>g has a favorable environmental profile even without consider<strong>in</strong>g the<br />

credit for co-products for a 27% recycl<strong>in</strong>g rate. In this recycl<strong>in</strong>g rate, the maximum <strong>in</strong>crease <strong>in</strong> environmental impacts<br />

analysed was 5%.<br />

However, while the approach used does not represent the real situation and presents m<strong>in</strong>or scientific uncerta<strong>in</strong>ties,<br />

it is extremely important to f<strong>in</strong>d solutions for modell<strong>in</strong>g recycl<strong>in</strong>g processes <strong>in</strong> order to account for<br />

all the co-products from the cha<strong>in</strong>. The existence of these co-products makes this reverse logistic cha<strong>in</strong> economically<br />

viable.<br />

5. Conclusion<br />

Based on the results of this study, it is possible to state: The <strong>in</strong>crease <strong>in</strong> the process efficiency ma<strong>in</strong>ly due to<br />

the modernisation of liquid packag<strong>in</strong>g board manufactur<strong>in</strong>g brought a reduction of 20% of total energy consumption<br />

compared with the same functional units <strong>in</strong> 2000.<br />

The <strong>in</strong>crease <strong>in</strong> the recycl<strong>in</strong>g rate up to 70% could still br<strong>in</strong>g about energy benefits even consider<strong>in</strong>g the consumption<br />

of new natural resources and air/water emissions related to the logistic reverse cha<strong>in</strong>.<br />

A comparison of the years 2000 and 2011 shows that for the current recycl<strong>in</strong>g rate of 27% compared with no<br />

recycl<strong>in</strong>g the follow<strong>in</strong>g reductions could be observed: 23% <strong>in</strong> global warm<strong>in</strong>g, 8% <strong>in</strong> abiotic depl<strong>et</strong>ion, 13%<br />

<strong>in</strong> acidification, 15% <strong>in</strong> photochemical ozone creation, 11% <strong>in</strong> human toxicity and 8% <strong>in</strong> eutrophication<br />

measured by the functional unit of 1,000 litres of milk packag<strong>in</strong>g.<br />

The cha<strong>in</strong> analysed <strong>in</strong> this study is not only a hypoth<strong>et</strong>ical model but also represents almost all the <strong>in</strong>dustrial<br />

plants <strong>in</strong>volved <strong>in</strong> this cha<strong>in</strong>. This is the result of T<strong>et</strong>ra Pak efforts dur<strong>in</strong>g the last two decades f<strong>in</strong>d<strong>in</strong>g partners<br />

who could implement these processes and to make the recovery of their post consumer packages an<br />

economic, environmental and socially viable solution.<br />

6. Acknowledgments<br />

The authors are grateful to T<strong>et</strong>ra Pak by provid<strong>in</strong>g data and valuable discussions for this work. Authors are<br />

also grateful for f<strong>in</strong>ancial support of this company, to Fapesp who f<strong>in</strong>anced the first <strong>LCA</strong> study for CETEA<br />

<strong>in</strong> 1998 and for the f<strong>in</strong>ancial support of travell<strong>in</strong>g expenses.<br />

7. References<br />

Berl<strong>in</strong>, J., 2002. Environmental life cycle asseessmentg (<strong>LCA</strong>) of Swedish semi-hard cheese. International Dairy journal 12, 939-953.<br />

Coltro, L., Castilho, G., Garcia, E.E.C., 2003. Life Cycle Inventory for Electric Energy System <strong>in</strong> Brazil. Int. J. <strong>LCA</strong>, 8(5), 290-296.<br />

Falkenste<strong>in</strong> E.V., Wellenreuther F., D<strong>et</strong>zel, A.(2010) <strong>LCA</strong> studies compar<strong>in</strong>g beverage cartons and alternative packag<strong>in</strong>g: can overall<br />

conclusions be drawn? Int. J. <strong>LCA</strong>, 15, 938–945.<br />

Gatti, J.B., Castilho, G., Garcia, E.E., 2000. Análise de Ciclo de Vida de produtos de alumínio (Available <strong>in</strong> Portuguese language,<br />

confidential document for <strong>in</strong>ternal use), CETEA/ITAL, Camp<strong>in</strong>as. Relatório CETEA P004/00, 88p.<br />

Gu<strong>in</strong>ée, J. B. <strong>et</strong> al., 2001. Life Cycle Assessment – An operational Guide to the ISO Standards. Leiden.<br />

Hospido, A., Moreira, M.T., Feijoo, G., 2003. Simplified life cycle assessment of Galician milk production. International Dairy<br />

Journal 13, 783e796.<br />

International Organization for Standardization – ISO, 2006. Environmental management – Life cycle assessment – Pr<strong>in</strong>ciples and<br />

framework – ISO 14040. Genève/Switzerland: ISO, 44p.<br />

International Organization for Standardization - ISO 14049, 2000. Environmental management – Life cycle assessment – Examples<br />

of ISO 14041 to goal and scope def<strong>in</strong>ition and <strong>in</strong>ventory analysis, Genève/Switzerland, 44p<br />

Mourad A.L. <strong>et</strong> al., 2000. Análise de Ciclo de Vida de Embalagens para o Mercado Brasileiro, Relatório S<strong>et</strong>orial ABPO – Associação<br />

Brasileira de Papelão Ondulado (Available <strong>in</strong> Portuguese language, confidential document for <strong>in</strong>ternal use), CETEA/ITAL;<br />

Camp<strong>in</strong>as, 1-120.<br />

Mourad, A.L., Garcia, E.E.C., Vilela, G.B., Zuben, F., 2008a. Environmental effects from a recycl<strong>in</strong>g rate <strong>in</strong>crease of cardboard of<br />

aseptic packag<strong>in</strong>g system for milk us<strong>in</strong>g life cycle approach. Int. J. <strong>LCA</strong> 13, 140-146.<br />

279

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

Saved successfully!

Ooh no, something went wrong!