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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 />

tubErreur ! Source du renvoi <strong>in</strong>trouvable.Erreur ! Source du renvoi <strong>in</strong>trouvable.Erreur ! Source du<br />

renvoi <strong>in</strong>trouvable.. The authors experience is that once opened the large yogurt needs be consumed <strong>in</strong> a<br />

timeframe that is not always m<strong>et</strong>, where as the <strong>in</strong>dividual pack<strong>et</strong>s are consumed <strong>in</strong> one serv<strong>in</strong>g.<br />

Table 4. Two types of yogurt packag<strong>in</strong>g compared<br />

Packag<strong>in</strong>g (p) = 6 x 7 g PS a tubs<br />

= 42 x 3.97 g CO2-eq/g<br />

= 35 g PP a tub & lid + 2 g alum<strong>in</strong>ium a foil<br />

= 35 x 2.90 g CO2-eq/g + 2 x 12.57 g CO2-eq/g<br />

<strong>Food</strong> impact (f)<br />

= 166.7 g CO2-eq<br />

= 6 x 175 g yogurt<br />

= 126.7 g CO2-eq<br />

b<br />

= 900 g yogurt<br />

= 1 050 x 1.22 g CO2-eq/g<br />

= 1 281 g CO2-eq<br />

b<br />

Waste (w)<br />

= 900 x 1.22 g CO2-eq/g<br />

= 1 098 g CO2-eq<br />

c = 5% residual yogurt <strong>in</strong> pack = 30% yogurt (mouldy <strong>in</strong> fridge)<br />

Impact/pack = p + fw<br />

= p + fw<br />

= 166.7 + (1 281 x 5%) = 126.7 + (1 098 x 30%)<br />

= 230.8 g CO2-eq /6 pack = 456.1 g CO2-eq/900 g tub<br />

Impact/kg d = 219.8 g CO2-eq/kg = 506.7 g CO2-eq/kg<br />

a. impact factors from Eco<strong>in</strong>vent database (<strong>2012</strong>) us<strong>in</strong>g the Australian impact m<strong>et</strong>hod<br />

b. . L<strong>in</strong>denthal <strong>et</strong> al., (2010)<br />

c. emissions from the biodegradation of the wasted food were not considered <strong>in</strong> this model, if <strong>in</strong>cluded the emission factor for food<br />

waste would be higher<br />

d. functional unit of packag<strong>in</strong>g is the ‘delivery of consumed food per kg’<br />

The results <strong>in</strong>dicate that once food waste is <strong>in</strong>cluded the environmental impact differ substantially. In the<br />

yogurt example, the bulk 900g pack<strong>et</strong> has a 24% lower GWP than the 6 pack when viewed <strong>in</strong> isolation of<br />

food waste, and a 230% higher GWP when <strong>in</strong>cluded <strong>in</strong> the above scenario. Appropriate portion siz<strong>in</strong>g that<br />

reduce food waste has a dom<strong>in</strong>ant impact, even with a food type such as yogurt that has a relatively low<br />

GWP <strong>in</strong> comparison to meat based products.<br />

From a design perspective it is also possible to foresee that packag<strong>in</strong>g design to reduce food waste should<br />

not always result <strong>in</strong> an <strong>in</strong>crease <strong>in</strong> the environmental impact of packag<strong>in</strong>g <strong>in</strong> isolation. Traditional packag<strong>in</strong>g<br />

design solutions such as lightwieght<strong>in</strong>g and material selection could apply to make the 6 pack less material<br />

<strong>in</strong>tense than the 900 g tub.<br />

4. Discussion: Possible means to <strong>in</strong>tegrate food waste <strong>in</strong>to <strong>LCA</strong><br />

The results of the rice and yogurt case studies <strong>in</strong>dicate scenarios where <strong>in</strong>creases <strong>in</strong> packag<strong>in</strong>g may reduce<br />

the overall environmental impact by avoid<strong>in</strong>g food waste. The most critical data gap to successfully<br />

compl<strong>et</strong><strong>in</strong>g replicable <strong>LCA</strong>’s is <strong>in</strong> estimat<strong>in</strong>g the amount of food wasted. A very small variation <strong>in</strong> the percentage<br />

of food wasted that has a high GWP potential like red meat substantially differs the environmental<br />

impact of packag<strong>in</strong>g once food waste is <strong>in</strong>cluded. It is also acknowledge that packag<strong>in</strong>g is only one of many<br />

ways that food waste could be reduced. In a recent stakeholder engagement forum <strong>in</strong> Australia brand owners<br />

identified that they rarely compl<strong>et</strong>e user trials on how packag<strong>in</strong>g is actually used <strong>in</strong> the home (Verghese <strong>et</strong><br />

al., <strong>2012</strong>b). To test the success of alternate packag<strong>in</strong>g scenarios requires ‘additional fieldwork and empirical<br />

research outside the traditional boundaries of <strong>LCA</strong>’ (Verghese, <strong>et</strong> al., <strong>2012</strong>a, p. 403). Understand<strong>in</strong>g food<br />

waste <strong>in</strong> the home is a fundamental first step to improv<strong>in</strong>g the resolution of waste estimates. Multiple sensitivities<br />

can quickly be run by alter<strong>in</strong>g the percentage wasted and packag<strong>in</strong>g type to see the impact of reduced<br />

wastage and they can be used to develop hypothesis that require empirical test<strong>in</strong>g.<br />

The packag<strong>in</strong>g attributes that <strong>in</strong>fluence food waste elaborated <strong>in</strong> section 2 provide a useful guide for<br />

packag<strong>in</strong>g designers to assist them <strong>in</strong> design<strong>in</strong>g packag<strong>in</strong>g to faciliate reduced food waste. By tak<strong>in</strong>g a service<br />

perspective the focus can move from the product itself, to the process it is used for (Vargo and Lush,<br />

2004; Edvardsson <strong>et</strong> al., 2005). The product can be described by attributes, each attribute provid<strong>in</strong>g prerequisites<br />

for the service. Each packag<strong>in</strong>g attribute assists to script <strong>in</strong>dividual behaviour and experiences, and<br />

potentially the environmental outcome e.g. , the amount of food waste generated. The consumer <strong>in</strong>teraction<br />

with the product depends on the design of the product, the consumer preferences and experiences, and the<br />

context of the consumer (Löfgren, 2006).<br />

295

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