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AN INITIAL ASSESSMENT OF THE SUITABILITY OF<br />

TOTAL MAXIMUM DAILY LOADS (TMDLs) AS A MEANS<br />

OF MANAGING DIFFUSE POLLUTION UNDER THE<br />

WATER FRAMEWORK DIRECTIVE<br />

RJ Cooper 1 , RC Ferrier 1 , RD Harmel 2 , SJ Langan 1 , AJA Vinten 1 and MI Stutter 1<br />

1<br />

The Macaulay Institute, Craigiebuckler, Aberdeen, AB15 8QH, UK, E-mail: r.cooper@<br />

macaulay.ac.uk; 2 USDA-ARS, 808 E. Blackland Road, Temple, Tex<strong>as</strong>, 76502, USA<br />

SUMMARY<br />

In the United States, the control of diffuse pollution is addressed by the Total<br />

Maximum Daily Loads programme. In this paper, we <strong>as</strong>sess whether this programme<br />

is suitable for use under the Water Framework Directive, and identify two key issues<br />

concerning the setting of water quality standards and uncertainty.<br />

INTRODUCTION<br />

The Water Framework Directive (WFD) raises a number of challenges for water<br />

quality regulation in the UK, one of which concerns the identification, quantification<br />

and control of diffuse pollution inputs to water bodies. With the initial diffuse<br />

pollution characterisation and impacts analysis now complete, and the monitoring<br />

programmes about to be implemented, attention must now turn to the setting of<br />

environmental objectives and the design and implementation of programmes of<br />

me<strong>as</strong>ures (POMs) to control diffuse pollution inputs. While the WFD provides a<br />

b<strong>as</strong>is for the development of legislation in this respect, an appropriate regulatory<br />

framework h<strong>as</strong> yet to be established. In the United States (US), the control of diffuse<br />

pollution is addressed by the Total Maximum Daily Loads (TMDL) programme, which<br />

provides a framework within which linkages between diffuse pollution sources and<br />

impacts are <strong>as</strong>sessed, and permissible loads accordingly defined. The purpose of<br />

this paper is to introduce the TMDL concept, demonstrate its application using the<br />

Tarland Burn in NE Scotland <strong>as</strong> a c<strong>as</strong>e study, and discuss its suitability <strong>as</strong> a means<br />

of managing water quality under the WFD.<br />

THE TMDL CONCEPT<br />

Over the p<strong>as</strong>t 30 years, water quality management in the US h<strong>as</strong> focussed mainly<br />

on the control of point source pollution, via effluent-b<strong>as</strong>ed water quality standards<br />

established under the Clean Water Act (CWA). Although this h<strong>as</strong> resulted in a general<br />

improvement in water quality, in 2000 over 36 % of water bodies still did not meet<br />

the CWA goal of being ‘fishable, swimmable’, due to inputs of pollutants such <strong>as</strong><br />

nutrients and sediment from diffuse sources such <strong>as</strong> agriculture and urban runoff<br />

(Boyd, 2000). Consequently, there h<strong>as</strong> been a recent shift in the focus of water<br />

quality management from effluent-b<strong>as</strong>ed to ambient–b<strong>as</strong>ed water quality standards.<br />

This is the context within which the Environmental Protection Agency (EPA) is<br />

obligated to implement the TMDL programme, the objective of which is attainment<br />

of ambient water quality standards through the control of both point source and<br />

diffuse pollution.<br />

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