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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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GROUP 2, SESSION A: CARBON OR WATER FOOTPRINTS, SOIL, BIODIVERSITY 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 />

53. A simplified tool for the estimation of N and P emissions due to the<br />

use of fertiliser <strong>in</strong> a <strong>LCA</strong> study<br />

Filippo Sessa 1,* , Massimo Mar<strong>in</strong>o 1 , Pierluigi Meriggi 2 , Matteo Ruggeri 3 , Michele Zerb<strong>in</strong>i 4<br />

1 Life Cycle Eng<strong>in</strong>eer<strong>in</strong>g, 2 Horta srl, 3 Univerisità Cattolica del Sacro Cuore, Piacenza, 4 Barilla G. R. Fratelli<br />

S.p.a, Correspond<strong>in</strong>g author. E-mail: sessa@studiolce.it<br />

Emissions of nitrogen and phosphorus compounds from soil are among the most relevant sources of environmental<br />

impact <strong>in</strong> the life cycle of most agricultural products. The most important emissions <strong>in</strong> air are<br />

N2O, which has a high Global warm<strong>in</strong>g potential and NO and NH3 which contribute to acidification. The<br />

most important emissions <strong>in</strong> water are nitrates and phosphates, which contribute to eutrophication of water.<br />

Agricultural practices such as fertilisation and tillage could seriously affect these k<strong>in</strong>ds of emission.<br />

It is often difficult to estimate these emissions because they depend on a multitude of factors such as climate<br />

conditions, soil characteristics and cultivated crops. There are models <strong>in</strong> literature that enable to estimate<br />

them with a certa<strong>in</strong> precision but <strong>in</strong> many cases they are too complicated and require <strong>in</strong>put which would imply<br />

money and time efforts that are not always available <strong>in</strong> a life cycle study. On the other hand it is possible<br />

to estimate emissions us<strong>in</strong>g emission factors or equations which however are too simplistic and do not permit<br />

for example to appreciate differences among different farm<strong>in</strong>g systems. The aim of this study was to identify<br />

models that may be easy to handle and <strong>in</strong> the meanwhile enough accurate to take <strong>in</strong>to account the ma<strong>in</strong> factors<br />

that <strong>in</strong>fluence the emissions. This is important <strong>in</strong> particular when perform<strong>in</strong>g a Life Cycle Assessment<br />

on a farm or on a territory level. With the <strong>in</strong>dividuated models a tool was then developed to permit the life<br />

cycle analyst to g<strong>et</strong> the values of emissions by <strong>in</strong>sert<strong>in</strong>g a few required <strong>in</strong>puts. Particular attention <strong>in</strong> the<br />

choice of the models has been given to the responsiveness to different types and dosage of fertilisers.<br />

The models <strong>in</strong>dividuated are Bouwman <strong>et</strong> al. (2002) for direct N2O emissions, IPCC (2006) for <strong>in</strong>direct N2O<br />

emissions, Bouwman <strong>et</strong> al. (2002) for NH3 emissions from m<strong>in</strong>eral fertilisers, Dohler <strong>et</strong> al. (2002) for NH3<br />

emissions from organic fertilisers, Stehfest <strong>et</strong> al. (2006) for NO emissions, De Willigen (2000) for nitrates<br />

emissions and Prahsun (2006) for phosphorus emissions.<br />

Most of the <strong>in</strong>put required can be obta<strong>in</strong>ed by ask<strong>in</strong>g the farmer and by soil analysis. Other data required are<br />

the quantity of annual precipitation and the type of climate, which can be easily obta<strong>in</strong>ed from literature or<br />

from some m<strong>et</strong>eorological database. Some factors required by the models are taken from literature and provided<br />

<strong>in</strong> the tool.<br />

The result of the work was a tool that enables the life cycle analyst to easily g<strong>et</strong> quite accurate estimates of<br />

nitrogen and phosphorus emissions from agricultural soils. The development prospect for the tool could enrich<br />

the <strong>in</strong>ternal database to make it more specific for d<strong>et</strong>erm<strong>in</strong>ed crops or geographical areas.<br />

References<br />

Bouwman, A.F., Boumans, L.J.M., Batjes, N.H., 2002. Estimation of global NH3 volatilization loss from<br />

synth<strong>et</strong>ic fertilizers and animal manure applied to arable lands and grasslands. Global Biogechem. Cycles<br />

16(2), 1024.<br />

Bouwman, A.F., Boumans, L.J.M., Batjes, N.H., 2002. Model<strong>in</strong>g global annual N2O and NO emissions from<br />

fertilized fields. Glob Biogeochem Cycles. 16(4), 1080-1107.<br />

IPCC, 2006. Guidel<strong>in</strong>es for National Greenhouse Gas Inventories<br />

Prasuhn, V., 2006. Erfassung der PO4-Austräge für die Ökobilanzierung. SA<strong>LCA</strong>-Phosphor. Zürich, CH,<br />

Agrocope FAL Reckenholz.<br />

Stehfest, E., Bouwman, L., 2006. N2O and NO emission from agricultural fields and soils under natural<br />

veg<strong>et</strong>ation: summariz<strong>in</strong>g available measurement data and modell<strong>in</strong>g of global annual emissions. Nutrient<br />

Cycl<strong>in</strong>g <strong>in</strong> Agroecosystems. 74, 207-228.<br />

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