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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 1B: TOWARDS LIFE CYCLE SUSTAINABILITY ASSESSMENT 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 />

lated with economic and environmental performance. Moreover, only n<strong>in</strong>e INC farms were assessed. A<br />

higher number of farms is needed to improve robustness of compar<strong>in</strong>g the INC farm<strong>in</strong>g system, with conventional<br />

practices, especially consider<strong>in</strong>g the fact that variability with<strong>in</strong> the groups was substantial.<br />

For economic performance, no significant differences were seen. However, NFI was 44% higher for INC<br />

farms. High standard deviations <strong>in</strong>dicated that differences with<strong>in</strong> groups were higher than b<strong>et</strong>ween groups. It<br />

is common that economic performance differs highly among farms. There are also large fluctuations b<strong>et</strong>ween<br />

the years, which also affects the outcomes of our analyses. The year 2008 was a relatively prosperous year,<br />

whereas 2009 showed the lowest <strong>in</strong>come over the last decade (De Bont <strong>et</strong> al., 2009). INC farms received a<br />

higher <strong>in</strong>come due to higher payments from bird protection programmes and used a higher amount of own<br />

labour, which was not <strong>in</strong>cluded <strong>in</strong> NFI.<br />

For environmental performance, INC farms outperformed conventional farms on energy use and SOC.<br />

Us<strong>in</strong>g above-ground spread<strong>in</strong>g for slurry expla<strong>in</strong>s a lower on-farm energy use, because of lower diesel consumption<br />

application technique. On-farm acidification potential was expected to be higher due to a higher<br />

emission factor for aboveground spread<strong>in</strong>g. INC farms, however, applied less artificial fertiliser and had a<br />

hous<strong>in</strong>g system with a lower emission factor, compensat<strong>in</strong>g the higher emission of apply<strong>in</strong>g animal manure.<br />

SOC was significantly higher for INC farms, partly because these farms were reluctant <strong>in</strong> apply<strong>in</strong>g regular<br />

grassland renovation. Results from other studies however also show that SOC contents are strongly controlled<br />

by soil type, dra<strong>in</strong>age level and land use history, factors which are site-specific. Thus, the differences<br />

b<strong>et</strong>ween both groups with respect to SOC content cannot purely be related to differences <strong>in</strong> current farm<br />

management.<br />

For soci<strong>et</strong>al performance, current FADN does not have the potential to assess animal welfare us<strong>in</strong>g preferred<br />

animal-based <strong>in</strong>dicators. Pasture hours, therefore, were used as an <strong>in</strong>direct <strong>in</strong>dicator for animal welfare.<br />

This <strong>in</strong>dicator showed no differences b<strong>et</strong>ween both farm types. INC farms significantly differed from<br />

conventional farms for received payments on ecosystem services. These payments, however, did not reflect<br />

the actual ga<strong>in</strong> <strong>in</strong> improved soci<strong>et</strong>al performance. A b<strong>et</strong>ter <strong>in</strong>dicator should be area based, or express<strong>in</strong>g biodiversity,<br />

e.g. number of plant species, or number of birds. The INC farms aims for improved nutrient cycl<strong>in</strong>g,<br />

by mak<strong>in</strong>g use of all available resources on-farm. This approach goes along with social <strong>in</strong>volvement<br />

and entrepreneurial complacency. These values, however, were not <strong>in</strong>cluded <strong>in</strong> this assessment.<br />

5. Conclusion<br />

INC farms positively differ from conventional farms <strong>in</strong> a lower non-renewable energy use, higher soil organic<br />

carbon and receiv<strong>in</strong>g higher payments for ecosystem services, without compromis<strong>in</strong>g on their economic<br />

performance. However, significant differences b<strong>et</strong>ween INC farms were limited, despite INC farm<br />

follow a farm<strong>in</strong>g practice aim<strong>in</strong>g at optimiz<strong>in</strong>g use of on-farm available resources. Overall, most performance<br />

<strong>in</strong>dicators did not show significant differences. High standard deviations <strong>in</strong>dicate that differences with<strong>in</strong><br />

groups are mostly higher than b<strong>et</strong>ween groups.<br />

6. References<br />

Anonymous, 2010a. Handreik<strong>in</strong>g bedrijfsspecifieke excr<strong>et</strong>ie melkvee, versie per 1 januari 2010 van kracht. M<strong>in</strong>istry of Economic<br />

Affairs, Agriculture and Innovation, The Hague.<br />

Anonymous, 2010b. Regel<strong>in</strong>g Ammoniak en Veehouderij (RAV), article 2. M<strong>in</strong>istry of Infrastructure and the Environment, The<br />

Hague.<br />

Blank, S. C., Erickson, K.W., Nehr<strong>in</strong>g, R., Hallahan, C., 2009. Agricultural profits and farm household wealth: a farm-level analysis<br />

us<strong>in</strong>g repeated cross sections. Journal of agricultural and applied economics 1: 207-225.<br />

Benn<strong>et</strong>, L.T., Mele, P.M., Ann<strong>et</strong>t, S., Kasel, S., 2010. Exam<strong>in</strong><strong>in</strong>g l<strong>in</strong>ks b<strong>et</strong>ween soil management, soil health, and public benefits <strong>in</strong><br />

agricultural landscapes: An Australian perspective. Agriculture Ecosystems & Environment 139: 1-12.<br />

De Bont, C.J.A.M, Van Everd<strong>in</strong>gen, W.H., Van der Knijff, A., Van der Meulen, H.A.B., 2009. Actuele ontwikkel<strong>in</strong>g van resultaten<br />

en <strong>in</strong>komens <strong>in</strong> de land- en tu<strong>in</strong>bouw <strong>in</strong> 2009. LEI, part of Wagen<strong>in</strong>gen UR. The Hague.<br />

Dekker, S.E.M., De Boer, I.J.M., Vermeij, I., Aarn<strong>in</strong>k, A.J.A., Groot Koerkamp, P.W.G., 2011. Ecological and economic evaluation<br />

of Dutch egg production systems. Livestock Science 139: 109-121.<br />

De Vries, M., Bokkers, E.A.M., Dijkstra T., Van Schaik, G., De Boer, I.J.M., 2011. Invited review: Associations b<strong>et</strong>ween variables<br />

of rout<strong>in</strong>e herd data and dairy cattle welfare <strong>in</strong>dicators. J. Dairy Science: 94:3213–3228.<br />

EU, 2006. Thematic Strategy for Soil Protection. Commission of the European communities, Brussels.<br />

Heijungs, R., Gu<strong>in</strong>ee, J.,Huppes, G., Lankreijer, R.M., Udo de Haes, H.A., Wagener Sleeswijk, A., Ansems, A.M.M., Eggels, P.G.,<br />

VanDu<strong>in</strong>, R., De Goede, H.P., 1992. Environmental Life Cycle Assessment of Products. Guide and backgrounds. CML, Institute<br />

for Environmental Sciences, Leiden.<br />

IPCC, 2007. In: Pachauri, R.K., Reis<strong>in</strong>ger, A.(Eds.), Core Writ<strong>in</strong>g Team, Intergovernmental Panel on Climate Change. Climate<br />

Change 2007: Synthesis Report. Contribution of Work<strong>in</strong>g Groups I, II and III to the Fourth Assessment Report of the Intergovernmental<br />

Panel on Climate Change. IPCC, Geneva.<br />

Nevedi, 2008-2009. L<strong>in</strong>eaire programmer<strong>in</strong>gen rundvee-, varkens- en pluimveevoeders. Monthly reports on feed composition computed<br />

by Schothorst Feed Research BV. Lelystad.<br />

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