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Informe El medio ambiente en Europa: Estado y perspectivas 2020

Informe El medio ambiente en Europa: Estado y perspectivas 2020

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PART 2

FIGURE 13.2

Development of the gross nitrogen balance, nitrogen use efficiency and gross value added, EU-27

Index (2005 = 1.00)

1.15

1.10

1.05

1.00

0.95

0.90

0.85

0

2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015

Gross Nitrogen Balance (GNB) Nitrogen Use Efficiency (NUE) Agri Gross Value Added (GVA Agri)

Notes:

GNB, gross nitrogen balance; NUE, nitrogen use efficiency; GVA (agri), agricultural gross value added (agricultural industry). GNB

and NUE are based on Eurostat data (aei_pr_gnb), Eurostat estimates for Estonia (2015), Romania and Croatia (2004-2014) Belgium,

Bulgaria, Denmark, Greece, Italy, Cyprus, Latvia, Lithuania, Luxembourg, Malta (2004-2015). GVA of the agricultural industry (values at

current prices) based on Eurostat data (tag00056), economic accounts for agriculture — values at current prices.

Source: EEA calculations based on Eurostat data. 2005 = 1.

from agricultural land, and nutrient

levels still exceed nutrient critical loads

in most of the EU. Looking ahead,

a decrease of 2.6 % in comparison

to 2008 is projected for the average

nitrogen surplus in the EU by 2030. The

largest fall in the surplus is projected in

regions where a reduction in livestock

herd size is expected (EC, 2017b).

Many factors can influence the

development of the nitrogen balance

and trends vary regionally. These

factors include ambitions to reduce

production costs, policy measures,

the availability and prices of different

types of nitrogen fertilisers and

livestock numbers (EC, 2011b;

Eurostat, 2018b). Efficiency gains

observed in Europe may have been

achieved by adapting nitrogen

management, such as changes in

fertiliser application techniques or by

more targeted selection of varieties

(Balafoutis et al., 2017; Schrijver, 2016;

Zarco-Tejada et al., 2014).

Technological developments have the

potential to enable more targeted use

of inputs. However, such synergies

between environmental and economic

interests do not occur when it comes

to the structure and diversity of

agricultural landscapes, and soil

quality and health. Efforts to increase

production efficiency and income

have resulted in increasing land

parcel sizes, a reduction in landscape

features and drainage of land. This

consolidation, increasing homogeneity

298 SOER 2020/Environmental pressures and sectors

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