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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 2C: QUANTIFICATION AND REDUCTION OF UNCERTAINTY 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 />

sentative <strong>in</strong>ventories and <strong>in</strong>herent uncerta<strong>in</strong>ty ranges for secondary foreground data from different sources,<br />

we here present a m<strong>et</strong>hodology for select<strong>in</strong>g and weight<strong>in</strong>g <strong>in</strong>ventory values, and <strong>in</strong> the meantime produce<br />

estimates for <strong>in</strong>herent uncerta<strong>in</strong>ty param<strong>et</strong>ers. The m<strong>et</strong>hodology will be practically exemplified by Brazilian<br />

soybean production, as soybeans often constitute more than 30% of aquaculture feeds.<br />

Materials and m<strong>et</strong>hods<br />

As the example here is assumed to rely upon the eco<strong>in</strong>vent v2.2 database for background data, the aim is to<br />

be consistent with choices made there<strong>in</strong>. Therefore, <strong>in</strong> parallel with eco<strong>in</strong>vent v2.2, the NUSAP approach<br />

described by Weidema and Wesnaes (1996) was adopted, categoris<strong>in</strong>g the orig<strong>in</strong>s of representativeness <strong>in</strong>to<br />

reliability, compl<strong>et</strong>eness, temporal correlation, geographical correlation and further technical correlation.<br />

The additional category of sample size and the assigned uncerta<strong>in</strong>ty factors suggested by Frischknecht <strong>et</strong> al.,<br />

(2007) were also implemented.<br />

As an <strong>in</strong>itial step, a decision tree was developed for foreground data, with a general dist<strong>in</strong>ction b<strong>et</strong>ween primary<br />

and secondary data (Erreur ! Source du renvoi <strong>in</strong>trouvable.1). The decision tree guides the practitioner<br />

towards recommended approaches when sourc<strong>in</strong>g process data, assum<strong>in</strong>g a default log-normal distribution<br />

of datas<strong>et</strong>s. Log-normal distributions are favoured as to avoid negative values, b<strong>et</strong>ter represent large<br />

variances and to be consistent with the eco<strong>in</strong>vent v2.2 database. Primary data are, moreover, prioritised as<br />

they are assumed to be up-to-date, highly relevant, and provide a higher level of d<strong>et</strong>ail. Secondary data are<br />

previously published data describ<strong>in</strong>g the process <strong>in</strong> focus, where the f<strong>in</strong>al selection of values should be <strong>in</strong>l<strong>in</strong>e<br />

with the goal and scope def<strong>in</strong>ition of the specific study at stake. Where relevant multiple secondary data<br />

sources exist, a weighted mean approach is recommended. Each outcome <strong>in</strong> the decision tree def<strong>in</strong>es a recommended<br />

type of mean, standard deviation and distribution, or alternative approaches <strong>in</strong> certa<strong>in</strong> cases.<br />

Figure 1. Decision tree for sourc<strong>in</strong>g unit process data for foreground processes.<br />

Weighted means b<strong>et</strong>ween secondary foreground param<strong>et</strong>ers were calculated us<strong>in</strong>g Weighted means<br />

( ) can be calculated from the aggregated means ( ) of samples (n), with the NUSAP derived geom<strong>et</strong>ric<br />

standard deviation used as the weight<strong>in</strong>g factor ( ). The <strong>in</strong>herent variability can, <strong>in</strong> turn, be calculated<br />

amongst the different param<strong>et</strong>ers where several sources exist. Miss<strong>in</strong>g values are excluded from the calculations<br />

and null values are calculated us<strong>in</strong>g 10% or the smallest value, due to the limitations of the logarithmical<br />

scale. To generate the f<strong>in</strong>al overall uncerta<strong>in</strong>ty param<strong>et</strong>er, the <strong>in</strong>herent geom<strong>et</strong>ric standard deviation<br />

needs to be summed with the most representative NUSAP <strong>in</strong>dicator for each <strong>in</strong>ventory flow (Frischknecht <strong>et</strong><br />

al., 2007).<br />

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