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five. These loadings are distributed among the significant sources of the pollutant<br />

of concern, with w<strong>as</strong>teload allocations containing the allowable loadings from point<br />

sources, and load allocations containing the allowable loadings from diffuse sources.<br />

A margin of safety is identified at this stage to take account of uncertainty in the<br />

analysis, although this is often arbitrarily determined rather than rigorously quantified.<br />

The margin of safety may be applied implicitly, using conservative <strong>as</strong>sumptions, or<br />

explicitly, by setting <strong>as</strong>ide a portion of the total loading capacity. Finally, in step six<br />

an implementation and monitoring plan is devised to oversee changes on the ground<br />

and determine whether the TMDL h<strong>as</strong> resulted in attaining the desired level of water<br />

quality. A conceptual overview of how the TMDL framework could be integrated with<br />

river b<strong>as</strong>in management planning under the WFD is presented in Figure 1.<br />

Figure 1: Conceptual overview of how water quality could be managed under<br />

the Water Framework Directive using the Total Maximum Daily<br />

Loads framework (in grey) <strong>as</strong> a means of regulation<br />

CASE STUDY: TARLAND BURN<br />

Introduction<br />

The Tarland Burn is a tributary of the River Dee in NE Scotland, and drains an area of<br />

intensive mixed land use. Agriculture in the lower zone of the catchment comprises a<br />

mosaic of arable fields and improved gr<strong>as</strong>sland, supporting cattle, sheep, barley and<br />

potato. The headwaters of the catchment feature steeper slopes comprising rough<br />

47

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