agriculture and ecosystem services - Serena
agriculture and ecosystem services - Serena
agriculture and ecosystem services - Serena
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
Relevance of OECDagri‐environmentalmeasures for PES%1009080706050403020100Figure 5Structure of agri-environmental payments in selected OECD countries in1996-1998 <strong>and</strong> 2006-20081996-98 2006-08 1996-98 2006-08 1996-98 2006-08 1996-98 2006-08EU NORWAY SWITZERLAND USAEU 15 for 1996-1998 <strong>and</strong> EU 27 for 2006-08LegendPayments based on input usePayments based on area/animal numbersTechnical assistance on farmsLong term resource (l<strong>and</strong>) retirementPayments based on a specific non-commodity outputAdapted from OECD, 2009It is notable that in Japan <strong>and</strong> Korea, both of which have relatively high levels of agriculturalpolicy support, agri-environmental schemes were introduced only relatively recently, while in othercountries, such as Mexico <strong>and</strong> Turkey, limited agricultural policy budgets have been prioritised forother purposes. However, Mexico also has a programme to encourage sustainable <strong>agriculture</strong>, whileTurkey has been introducing a series of initiatives to support organic farming over the last fiveyears. Korea has had a scheme to support reduced input use, including organic farming, initially(since 1999) in water catchment areas, but since 2002 extended across the whole country, withmeasures for environmentally-friendly livestock production introduced in 2004. Support for reducedinput use was only introduced in Japan in 2007 (OECD, 2009).Scope of the EU Common Agricultural Policy (CAP) <strong>and</strong>other OECD experiences on agri-environmental measuresIt is clear from the preceding review that, within the frameworks provided by the relevantregulations in the EU <strong>and</strong> other OECD countries, a wide range of approaches have been adopted,reflecting both local environmental priorities <strong>and</strong> resource availabilities, as well as differingpolicy perspectives on the roles that markets <strong>and</strong> policy interventions should play.51