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Table 2: Nutrient export from winter wheat and winter oilseed rape (2002)<br />

Land cover source<br />

~Area<br />

Ha<br />

% land<br />

cover<br />

Fertiliser<br />

Inputs (kg)<br />

Total export of<br />

nutrients (kg)<br />

W. wheat 4763 42.5 1000261 135736 47.5<br />

W. oilseed rape 549 4.9 115296 35091 12.3<br />

% of total loss of<br />

nutrients<br />

These results illustrate the significance of cereal cropping, and in particular the<br />

significance of winter sown crops to the problems of nutrient export in the catchment<br />

<strong>as</strong> a whole.<br />

In the monitored sub-catchments, the average annual loss of N ranged from 18.25<br />

to 164 mg/L. The highest N losses (> 146 mg/L p.a.) occur in are<strong>as</strong> contributing to<br />

gauging stations in sub-catchments where arable land use is more than 80% so this<br />

can be seen to be one of the contributing factors to such high losses. Potential risk<br />

of N loss w<strong>as</strong> attributed to each field plot by establishing which plots lie within 50 m<br />

of the watercourses and therefore pose the greatest threat to water quality. Using a<br />

combination of factors, the spatial distribution of N loss w<strong>as</strong> presented in ArcGIS <strong>as</strong><br />

risk maps to be used by stakeholders <strong>as</strong> part of a suite of land use decision-making<br />

tools.<br />

The Nutrient Export Risk Maps for the Leet Water Catchment<br />

Relative risk w<strong>as</strong> <strong>as</strong>signed using weighted values for a range of criteria; when<br />

these are combined with a weighting for proximity to a water-course, a combined<br />

risk score can be calculated. Weighting values ranging from 1–5 were given to the<br />

parameters shown in Table 3 below. For land use, nutrient input and export the full<br />

range of weighted values were available for each field. However, for distance from<br />

watercourse, the weight range w<strong>as</strong> restricted to reflect the significant contribution of<br />

field drains to potential nutrient loss.<br />

Table 3:<br />

Weighted values for parameters in risk <strong>as</strong>sessment<br />

Land use<br />

Nutrient input<br />

kg/ha/year<br />

Daily nutrient<br />

export N<br />

(mg/L)<br />

Distance from<br />

water course (m)<br />

Woodland 0 0–0.09 1<br />

Fallow/set-<strong>as</strong>ide 1–99 0.1–0.19 > 50 2<br />

Grazing 100–199 0.2–0.29 3<br />

Spring cereals 200–249 0.3–0.39 11–50 4<br />

Winter cereals > 250 > 0.4 0–10 5<br />

Weighted<br />

value for each<br />

variable<br />

This enabled a total risk <strong>as</strong>sessment score of up to a maximum of 20 points to be<br />

<strong>as</strong>signed to each field plot. Risk w<strong>as</strong> then cl<strong>as</strong>sified into five categories b<strong>as</strong>ed on<br />

the following intervals:<br />

Very low risk<br />

Low risk<br />

Medium risk<br />

High risk<br />

Very high risk<br />

1 – 4 points<br />

5 – 8 points<br />

9 – 12 points<br />

13 – 16 points<br />

17 – 20 points.<br />

261

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