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ASSESSING THE COST-EFFECTIVENESS OF<br />
INTEGRATED MEASURES TO DECREASE LOSS OF<br />
NITRATE, PHOSPHORUS AND FAECAL INDICATOR<br />
ORGANISMS<br />
M Shepherd 1 , S Anthony 1 , P Haygarth 2 , D Harris 1 , P Newell-Price 1 , S Cuttle 2 , B<br />
Chambers 1 and D Chadwick 2<br />
1<br />
ADAS, Gleadthorpe, Meden Vale, Mansfield, Notts, NG20 9PF, UK, E-mail: mark.<br />
shepherd@ad<strong>as</strong>.co.uk; 2 IGER, North Wyke, Okehampton, Devon, EX20 SB, UK<br />
SUMMARY<br />
The timetable for implementation of the Water Framework Directive requires best<br />
available information to be synthesised now. Cost-effectiveness is an important<br />
consideration when deciding what actions should be taken to control diffuse pollution<br />
losses from agriculture. This paper presents preliminary results from a toolkit for<br />
<strong>as</strong>sessing the cost-effectiveness of combinations of mitigation methods invoked<br />
by a range of policy options. It is a mix of simplified diffuse pollution models (to<br />
determine b<strong>as</strong>eline losses of nitrate, phosphorus and faecal indicator organisms),<br />
best available information on cost-effectiveness drawn from other projects and,<br />
using these building blocks, a cost-curve approach. The approach relies on expert<br />
judgement.<br />
INTRODUCTION<br />
Implementation of the Water Framework Directive and addressing diffuse water<br />
pollution from agriculture means identifying and implementing practical on-farm<br />
methods for mitigating losses of pollutants from land to water. Agricultural sources<br />
of diffuse pollution include nutrients (nitrogen and phosphorus), agrochemicals (plant<br />
protection products, veterinary medicines and biocides), sediment and pathogens<br />
(faecal indicator organisms and FIOs). Generally, we have a good understanding<br />
of the mitigation methods available to farmers (e.g. Vinten et al., 2005); recent UK<br />
projects have listed these methods, which can number over 50 (RPA, 2005). They<br />
range in complexity from something <strong>as</strong> simple <strong>as</strong> using a fertiliser recommendation<br />
system through to more complex (and expensive) approaches, such <strong>as</strong> installing a<br />
constructed wetland.<br />
Research shows that combinations of mitigation methods will be needed to reduce<br />
losses to acceptable limits (Shepherd and Chambers, 2006). The challenge is now<br />
to ‘encourage’ land managers to implement these mitigation methods. Me<strong>as</strong>ures (or<br />
‘policy options’) to encourage uptake range from voluntary to regulatory (Table 1).<br />
To inform the debate, an understanding of the cost-effectiveness of these policy<br />
options is also important. This paper puts forward a methodology for determining the<br />
cost-effectiveness of combinations of mitigation methods (which could be brought<br />
about by different policy options). This novel approach allows an <strong>as</strong>sessment of<br />
combinations of me<strong>as</strong>ures and their effectiveness for controlling losses of nitrate,<br />
phosphorus and FIOs. Here, we present some preliminary results.<br />
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