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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 />

Compar<strong>in</strong>g <strong>in</strong>tegral susta<strong>in</strong>ability performance of conventional farms<br />

with farms focuss<strong>in</strong>g on <strong>in</strong>ternal recycl<strong>in</strong>g of nutrients<br />

80<br />

Mark A. Dolman 1,2,* , Marthijn P.W. Sonneveld 3 , Herman Mollenhorst 2,4 , Imke J.M. de Boer 2<br />

1 Agriculture Economics Research Institute, part of Wagen<strong>in</strong>gen University and Research centre, The Hague, The N<strong>et</strong>herlands<br />

2 Animal Production Systems Group, Wagen<strong>in</strong>gen University, Wagen<strong>in</strong>gen, The N<strong>et</strong>herlands<br />

3 Soil Geography and Landscape Group, Wagen<strong>in</strong>gen University, Wagen<strong>in</strong>gen, The N<strong>et</strong>herlands<br />

4 Bus<strong>in</strong>ess Economics Group, Wagen<strong>in</strong>gen University, Wagen<strong>in</strong>gen, The N<strong>et</strong>herlands<br />

Correspond<strong>in</strong>g author. E-mail: mark.dolman@wur.nl<br />

ABSTRACT<br />

Susta<strong>in</strong>able milk production systems require economically viable, environmentally sound and socially acceptable practices. We<br />

compared susta<strong>in</strong>ability <strong>in</strong>dicators of a group of conventional farms with a group of farms aim<strong>in</strong>g at improved <strong>in</strong>ternal nutrient cycle<br />

(INC) on their farm. Economic performance was based on n<strong>et</strong> farm <strong>in</strong>come (NFI) and labour productivity. Environmental performance<br />

<strong>in</strong>dicators were derived from a cradle-to-farm-gate life cycle assessment, i.e., land occupation (LO), non-renewable energy use<br />

(NREU), global warm<strong>in</strong>g potential (GWP), acidification potential (AP) and eutrophication potential (EP). Moreover, soil- and water<br />

quality were monitored. Soci<strong>et</strong>al performance was quantified with payments for ecosystem services, graz<strong>in</strong>g hours and penalties for<br />

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

organic carbon and receiv<strong>in</strong>g higher payments for ecosystem services, without compromis<strong>in</strong>g on economic performance. High standard<br />

deviations for other <strong>in</strong>dicators suggest that differences with<strong>in</strong> both groups are mostly higher than b<strong>et</strong>ween groups.<br />

Keywords: susta<strong>in</strong>ability, FADN, dairy farm<strong>in</strong>g, nutrient cycl<strong>in</strong>g<br />

1. Introduction<br />

A commonly used def<strong>in</strong>ition on susta<strong>in</strong>ability is to me<strong>et</strong> the needs of current generations without<br />

compromis<strong>in</strong>g the ability of future generations to me<strong>et</strong> their needs and aspirations (WCED, 1987).<br />

Susta<strong>in</strong>able milk production systems require economically viable, environmentally sound and socially<br />

acceptable practices (Thomassen <strong>et</strong> al., 2009). Besides deliver<strong>in</strong>g mark<strong>et</strong>able products, the delivery of<br />

products and services related to the quality of the environment, i.e. ecosystem services, is becom<strong>in</strong>g<br />

<strong>in</strong>creas<strong>in</strong>gly important. Such services <strong>in</strong>clude the value of the landscape and the contribution to biodiversity,<br />

water storage and supply of clean groundwater (MEA, 2005). Soil quality is a key aspect with respect to<br />

ecosystem services (Benn<strong>et</strong> <strong>et</strong> al., 2010). Land use by agriculture, however, rapidly <strong>in</strong>tensified, caus<strong>in</strong>g<br />

d<strong>et</strong>erioration of soil structure, impoverishment of the soil and a decl<strong>in</strong>e <strong>in</strong> soil organic matter (EU, 2006).<br />

This d<strong>et</strong>erioration of soil quality threatens the future food production and other important ecosystem<br />

services. The supply of ecosystem services <strong>in</strong> the N<strong>et</strong>herlands is orig<strong>in</strong>at<strong>in</strong>g from specific landscapes, for<br />

example the National Landscape ‘Noordelijke Friese Wouden (NFW)’ <strong>in</strong> the North of the N<strong>et</strong>herlands.<br />

Several farmers <strong>in</strong> this area follow a farm<strong>in</strong>g practice, aim<strong>in</strong>g at an improved <strong>in</strong>ternal nutrient cycle (INC) on<br />

their farm. In order to m<strong>in</strong>imize use of external <strong>in</strong>puts, INC farms focus on optimiz<strong>in</strong>g use of on-farm<br />

available resources, for example, soil organic matter, nutrients from manure and home-grown feed<br />

production (Van Hees <strong>et</strong> al., 2009). INC farms, therefore, can make a significant contribution to preservation<br />

of food produc<strong>in</strong>g capacity, while additionally produc<strong>in</strong>g ecosystem services. An <strong>in</strong>tegral assessment that<br />

quantifies the effect caused by this INC approach, however, is never performed. Several studies have<br />

assessed the environmental performance of INC farms <strong>in</strong> the past (Sonneveld <strong>et</strong> al., 2008). So far, however,<br />

no life cycle assessment (<strong>LCA</strong>) of INC farms has been performed. Moreover, an <strong>in</strong>tegral assessment,<br />

<strong>in</strong>clud<strong>in</strong>g economic, environmental, and soci<strong>et</strong>al <strong>in</strong>dicators has never been performed.<br />

The objective of this study, therefore, is to quantify the economic, environmental and soci<strong>et</strong>al<br />

performance of INC farms <strong>in</strong> the NFW and, secondly, benchmark with a conventional milk production<br />

system comparable <strong>in</strong> terms of farm size, <strong>in</strong>tensity and site-specific circumstances.<br />

2. M<strong>et</strong>hods<br />

2.1. Data<br />

Data needed to quantify economic, environmental and soci<strong>et</strong>al <strong>in</strong>dicators of farms were derived from the<br />

farm accountancy data n<strong>et</strong>work (FADN) and the M<strong>in</strong>erals Policy Monitor<strong>in</strong>g Programme. We quantified a<br />

two-year average susta<strong>in</strong>ability performance of n<strong>in</strong>e INC farms (2008-2009). For every INC farm, a conventional<br />

‘mirror-farm’ was composed from farms <strong>in</strong> FADN, us<strong>in</strong>g statistical match<strong>in</strong>g. Central assumption for<br />

statistical match<strong>in</strong>g is that farms resembl<strong>in</strong>g for the imputation variables, also resemble for the goal variables,<br />

<strong>in</strong> this case susta<strong>in</strong>ability performance <strong>in</strong>dicators (Vrolijk <strong>et</strong> al., 2005). For every INC farm, ten similar

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