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significant number of arable fields adjacent to the water course without any buffers.<br />

Therefore the majority of fields are cl<strong>as</strong>sified <strong>as</strong> high or very high risk. With the<br />

implementation of a 50-m buffer, risk is reduced to low. When applied to the whole<br />

of the catchment there is a net reduction of total N losses of 1.86%. However,<br />

implementing such large buffers may not be acceptable to farmers with smaller<br />

farming units <strong>as</strong> this will remove a greater proportion of their land from economic<br />

production.<br />

The second scenario investigated reducing fertiliser use (by 10% or 20%) on the<br />

existing land use regime. The results found that nutrient losses for the whole of<br />

the catchment were 8.8% and 17.5% respectively. The third scenario examined<br />

the impact of a radical change in land use. Table 5 shows that if all arable land use<br />

w<strong>as</strong> changed to permanent p<strong>as</strong>ture (i.e. only livestock farming is practiced), nutrient<br />

losses are predicted to be 55% less than they would be under the current intensive<br />

arable regime. However, a livestock-dominated farming system is not popular. This<br />

is because cereal production is seen to be more profitable than livestock farming.<br />

But more importantly to the farming community, the recent outbreak of foot and<br />

mouth dise<strong>as</strong>e and previous impacts of BSE have shown how vulnerable livestock<br />

can be to contagious or infectious dise<strong>as</strong>es and farmers would be very reluctant to<br />

specialise.<br />

The final scenario is the most radical model, requiring all agricultural land (including<br />

p<strong>as</strong>ture land) to be taken out of production and converted to woodland. Although this<br />

would reduce the current annual nutrient loss from approximately 902 to 111 mg/L,<br />

the economic, social and environmental impacts are extreme. Assuming plantation<br />

woodland takes over, this takes upward of 30 years to mature before felling takes<br />

place and an economic return made, so this would not be economically viable for<br />

the current farming community. In terms of social change, the range of employment<br />

activities in the local area would alter <strong>as</strong> the specialised skills of forestry workers<br />

and the number of workers required change. In environmental terms, although<br />

nitrate losses would reduce, there would be incre<strong>as</strong>ed acidification of water courses,<br />

leading to a decline of aquatic biodiversity. Terrestrial biodiversity would also change<br />

<strong>as</strong> existing wildlife habitats were destroyed.<br />

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