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Animal Waste, Water Quality and Human Health

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180<strong>Animal</strong> <strong>Waste</strong>, <strong>Water</strong> <strong>Quality</strong> <strong>and</strong> <strong>Human</strong> <strong>Health</strong>for which high- <strong>and</strong> low-flow FIO data were available for the summer bathingseason <strong>and</strong> 11 sites for which parallel winter data were available.Satellite-derived l<strong>and</strong> use data were used to characterise the catchment l<strong>and</strong> useupstream of these monitoring sites. These data have been used to deriverelationships between l<strong>and</strong> use <strong>and</strong> water quality during both high- <strong>and</strong> low-flowconditions <strong>and</strong> to quantify the effects of seasonality on FIO transport. This isimportant with respect to non-seasonal water uses such as abstraction fordrinking-water, particularly private supplies, <strong>and</strong> where receiving waters areused for shellfish harvesting. Table 5.8 presents the observed transport rates ofFIOs from these catchments expressed as faecal indicator concentrationobserved at catchment outlets with different l<strong>and</strong> uses in the UK summer <strong>and</strong>comparative winter data for 11 catchments. Table 5.9 expresses these data asexport coefficients which are the more common requirement of catchmenttransport models.The information in Tables 5.8 <strong>and</strong> 5.9 represent an attempt to provide themodelling community with a peer-reviewed accessible data resource to drivecatchment microbial transport models. They are, of course, regionally specific,highly biased to the developed nations <strong>and</strong> narrowly restricted to FIOs, that isnot having pathogen transport data <strong>and</strong> certainly not having specific informationdescribing zoonotic pathogen transport. The current status of transport data forthe FIO microbial parameters could compare with that available for the nutrientparameters some 25 years ago in North America (see e.g. PLUARG, 1983).5.5 CONCLUSIONS(1) Nutrient transport, as quantified by the export coefficient approach withina GIS, is exemplified for nitrogen by Mattikalli <strong>and</strong> Richards (1996). Inmany respects, this parallels the drivers of microbial transport outlinedin Kay et al. (2005, 2008b) in the United Kingdom. Other literaturesources of export coefficient for the FIOs are not, at present, available.However, it should be noted that FIO transport is highly episodic innature <strong>and</strong> highly seasonal. Thus, coefficients for high <strong>and</strong> low flow <strong>and</strong>for winter <strong>and</strong> summer are likely to be needed in addition to coefficientsfor different l<strong>and</strong> use types. For large-scale catchment appraisal, thisapproach is likely to provide sufficient detail for the policy communitywishing to prioritise “measures” designed to reduce FIO concentrations<strong>and</strong> where the key questions relate to the balance between point <strong>and</strong>diffuse inputs <strong>and</strong> the likely impact of specific interventions e.g.enhanced attenuation <strong>and</strong> storage to prevent sewerage system spills

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