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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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