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Costs of Reducing Nitrogen leaching from Agriculture when implementing the WFD in Denmark. Senior Researcher Brian H. Jacobsen Institute of Food and Resource Economics University of Copenhagen E-mail: Brian@foi.dk. Content. Danish background What have we done in DK ?
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Costs of Reducing Nitrogen leaching from Agriculture when implementing the WFD in Denmark Senior Researcher Brian H. Jacobsen Institute of Food and Resource Economics University of Copenhagen E-mail: Brian@foi.dk
Content • Danish background • What have we done in DK ? • Detailed regulation- but how ? • Conclusions
Analysis prior to WFD implementation • Denmark has implemented 3 actions plan with focus on nitrogen (50% reduction in N-leaching – large effect on point source) • Action Plan II in 1998 was followed by economic analysis (FOI report 169) • Action Plan III in 2003-4, based on detailed work on scenarios and economics of different measures. Midterm 2008. • - FOI report 167 and www.vmp3.dk
Danish – Dutch implementation • Danish focus on N, NL more focus on P • Fertiliser accounts vs MINAS (surplus) • - good idea, but….. • The need for control with animal manure (costs) and self-complience (avoid fraud) • Derogation for the Nitrate Directive (2.5 LU/ha) on 45% of the area in NL whereas it is 2.3 LU/ha on 4% of the area in DK. • N application similar on sandy soils, but higher in NL on clay soils • DK 10-15% below economic optimum
N-surplus, N-leaching and N-loss in DK WFD target
Steps in implementation Target 2015 Baseline 2015 Action Plan III Scattered housing and sewage Present condition Nitratedirective
Steps in implementation Target 2015 N-quota model Noatumncultivation Organicfarming Wetlands Catchcrops Baseline 2015 Action Plan III Sewage from scattered housing Present condition Nitratedirective
Fødevareøkonomisk Institut Denmark 4 water districts and 23 main catchment areas
Choosing measures in DK • Step 1: Make a list of all possible measures • Step 2: Analyse the effectiveness and costs of selected measures also looking at : • - Side effects (CO2, NH3, pestides, Biodiversity) • - Certainty with respect to estimates • - Budget and socio- economic costs • DMU report no. 625 from 2007 • Detailed analysis on the use of cost-effectiveness in FOI report no. 191.
Choosing measures in DK • Step 3: Select the most cost-effective measures for detailed analysis (3 regions) in 2008 • - likely potential • - administrative costs • - control issues • Step 4: An element in Green Growth (2009) • - Water, CO2, NH3 and Biodiversity plans • - Search for synergies • - Co-operation between ministries takes time • - Draft analysis of reduction requirements in catchments • - Implementation is difficult • Step 5: RBMP (2011?) • Step 6: Local action plans (2012?)
Division of marine area according to knowledge level ():V1-area (10%)V2-area (20%)V3-area (30%)In the 1st plan period focus is mainly on measures in V1 and V2
Reduction requirement Efterafgrøder FOI og DJF antager få sædskifteændringer og jævn placering i DK DMU angiver at der er plads til flere efterafgrøder (250-500.000 ha) Andel stiger fra 10/14% op til et gennemsnit på ca. 22%. (maks. 37%) (V1+V2 er 70% af det samlede areal) Arealet med yderligere 24% efterafgrøder er ca. 6% af arealet (Jylland). Areal med yderligere 0-5% er noget større. Stor geografisk forskellighed
Catchcrops in waterplans 2010 Efterafgrøder Add. Catch crops (%)
Danish – Dutch WFD implementation • Both has a need for large reductions in nutrient losses • NL focus on physical changes as N is believed to have been solved and P is too costly? • Agricultural measures in NL are relative few • Likely WFD exemptions are required in NL in 2027, DK have aimed more for 2015/2021.
NICA research project N-loss to the aquatic environment has to be reduced by up to 50% 2/3 of the N lost from the root zone disappears on the way, but when and where ? Uniform regulation is not efficient, but can we point to the robust areas ? What is the certainty of these predictions (scale) and economic gain ?
The Ringkøbing Fjord analysis Jacobsen et al., 2009
Target : Increased certainty and fewer costs related to mapping
Model approach : Newer, better and cheaper technologies to asses N-flow
Conclusions • The low hanging fruits have been picked • Synergy between measures for environmental policies is good, but does delay the process • Implementation of measures has proven to be a challenge • The DK approach to WFD is top-down and so local action plans are less required • Local participation might help to engage farmers more, but it is time consuming • Regulation based on field level knowledge requires good data and control