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Animal Waste, Water Quality and Human Health

Animal Waste, Water Quality and Human Health

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Exposure interventions 285domesticated animal populations. Increased human exposures may occur as aresult of increased leisure travel to regions where water-related diseases such asschistosomiasis, leptospirosis <strong>and</strong> others are endemic. The global nature of themarketplace also provides opportunities for the spread of disease: from wildpopulations to closely-associated domestic populations <strong>and</strong> ultimately a widergeographic spread through the transport of goods (Fouchier et al. 2005).Changes in human demographics at regional, national <strong>and</strong> global levels will beanother confounding factor, again possibly exacerbated by climate change <strong>and</strong>effects resulting from displacement or changes to human migration patterns(Hess et al. 2008).In spite of limitations imposed by current faecal indicator assessments <strong>and</strong> thedifficulties in relating pathogen burden to human exposure risk in a definitive way,the need for intervention (management of the physical environment <strong>and</strong> of humanbehaviour) still exists. Adequate protection of public health necessitates themitigation or elimination of the pollution source or the prevention of exposurewhenever real human health risks exist. Early hazard detection <strong>and</strong> riskattribution are necessary <strong>and</strong> relevant to evidence-based interventions, rangingfrom herd management (both farmyard <strong>and</strong> field measures), to downstream bestmanagement practices, to regulation <strong>and</strong> policy development, <strong>and</strong> theimplementation of public education campaigns. The st<strong>and</strong>ardization of a stepwiseinvestigative framework may support the targeting of these interventions<strong>and</strong> a logical progression may include the following:• Step 1 – develop an investigative framework for waterborne diseaseexposure interventions requiring the identification of credible microbialpathogens in the aqueous environment capable of causing disease inhumans (see: Chapter 2).• Step 2 – identification of a conveyance mechanism (water, sediments,intermediary hosts) capable of delivering the pathogen (see: Chapter 5,Haack et al. 2003); establishing an exposure route connecting the humanhost to the source (see: Chapter 7).• Step 3 – determine an attributable practice (i.e. agricultural, animalhusb<strong>and</strong>ry, recreational, or cultural) which may be managed with theanticipated outcome being the reduction of the transmission risk <strong>and</strong>,ultimately of the disease burden.Management of pollutant sources or the affected populations does not comewithout cost <strong>and</strong> any intervention must weigh the expenditure against the direct<strong>and</strong> indirect economic benefits (see: Chapter 12) <strong>and</strong> feasibility of a sustainedpositive outcome. The carbon cost of different mitigation options may also beconsidered, comparing, for example, the pouring of concrete <strong>and</strong> pumping

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