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ESTIMATING DIFFUSE PHOSPHORUS LOADS TO<br />

LAKES: IMPLICATIONS FOR THE CALCULATION OF<br />

TOTAL MAXIMUM DAILY LOADS<br />

LH Defew<br />

Centre for Ecology and Hydrology, Bush Estate, Penicuik, Midlothian, EH26 0QB,<br />

UK, E-mail: ldef@ceh.ac.uk<br />

SUMMARY<br />

Nutrients and the concentrations in which they are present within a water body<br />

are important factors regulating the growth of phytoplankton and other plants.<br />

Problematic overgrowth of these is generally recognised <strong>as</strong> the biological<br />

manifestation of eutrophication and poor water quality, often resulting in hypoxia,<br />

loss of biodiversity, fish kills, and rele<strong>as</strong>e of algal toxins in the water body. As many<br />

freshwater environments are considered to be phosphorus limited, controlling and<br />

regulating the input of this particular nutrient is often one of the targets set under the<br />

total maximum daily load (TMDL) management approach.<br />

A TMDL is the sum of the allowable loads of a single pollutant from all contributing<br />

point and non-point (diffuse) sources, including natural background levels. The major<br />

steps in the American TMDL initiative are: (1) to develop load calculations for nonpoint<br />

sources of pollution; (2) to calculate natural loads; (3) to calculate maximum<br />

total loads from all sources; and (4) to determine how to reduce the maximum load<br />

in order to meet water-quality standards. A key requirement of this approach is the<br />

determination of accurate and reliable pollutant loads to the receiving water from<br />

non-point sources.<br />

Many of the methods that are currently being developed in the UK to <strong>as</strong>sess nutrient<br />

inputs to lakes from non-point sources are b<strong>as</strong>ed on data collected at weekly, monthly<br />

or even quarterly intervals. Previous studies have shown that such infrequent data<br />

collection results in pollutant load estimates that are of low accuracy and precision<br />

(Webb et al., 1997; Soerens and Nelson, 2001). There is now mounting evidence<br />

(e.g. May et al., 2005) that calculations b<strong>as</strong>ed on such data may underestimate the<br />

pollutant load to water bodies from diffuse sources by up to 80%. This is because<br />

they fail to take account of the influence of storm events on the mobilisation and<br />

transport of pollutants. The method used to estimate the nutrient loading to a lake<br />

will have important implications to the final TMDL that is calculated. To be reliable,<br />

TMDLs must take into account the impact of high intensity, low frequency rainfall<br />

events on nutrient loadings to water bodies.<br />

205

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