Water, sanitation, hygiene & health: Implications for MUS approaches Jenna Davis Stanford University 26 April 2006 Davis 2006 Outline A historical note Health impacts of water-related illness Classification of water- and sanitationrelated disease The quantity/quality debate Implications for MUS approaches Davis 2006 A historical note Modern W&S networks were first developed out of concerns for public health Debate regarding cause of illness (pythogenic versus germ theory of disease) Beliefs (and misunderstandings) about exposure routes shaped investment priorities, development of W&S infrastructure Davis 2006 W&S services and health Direct effects Half the developing world suffering from a water- or sanitation-related disease (UNICEF) 3-7 million deaths each year (WHO) Indirect effects Injuries Foregone child care Davis 2006 Types of water- and sanitation-related disease (WHO) Water-borne: Contaminated water or food (e.g., cholera) Water-based: Parasites within water habitat (e.g., Guinea worm, schistosomiasis) Water-washed: Inadequate hygiene (e.g., trachoma) Water-related: Insects near water habitat (e.g., malaria, dengue) Davis 2006 Annual morbidity 384,000 Annual mortality 11,000 Cholera Waterborne Typhoid Waterborne 5,000,000 125,000 Dracunculiasis (Guinea worm) Schistosomiasis (bilharzia) Waterbased 11,500 <1,000 Waterbased 200,000,000 300,000 Trachoma Waterwashed 500,000,000 - Malaria Waterrelated 400,000,000 1,500,000 Dengue Waterrelated 50,000,000 200,000 WHO data, 1997-2004 Davis 2006 What about diarrhea? Most prevalent W&S service-related disease 4 billion cases annually, 1.8 million deaths (2004); ~90% of victims are children <5 4% of all deaths and 6% of health loss to disability Both waterborne and water-washed types exist—debate as to which is more prevalent Davis 2006 Is the etiology of diarrhea so important? Global deaths per year Water-borne diarrhea Water-washed diarrhea Other water-borne Other water-washed Water-based Water-borne Water-washed Water-based Water-related Water-related Davis 2006 Controlling waterborne diseases requires access to a water source of high quality Controlling water-washed diseases depends on easy access to large quantities of water and good hygiene practices Controlling water-based diseases depends on elimination of contact with the infected water source Controlling water-related diseases depends on decreased exposure to the vector Davis 2006 Beliefs (and misunderstandings?) about the relative contribution of different exposure routes are shaping investment priorities, development of W&S infrastructure Davis 2006 Significance of this debate for MUS? Where MUS involves irrigation and other uses with freshwater (“productive plus”), growing consensus on quantity over quality in the W&S sector is good news. Net health impacts likely to be positive, even absent concomitant water treatment investment Implies few substantial institutional / regulatory changes (pubic health perspective) Exceptions might include pesticide contamination Davis 2006 Significance of this debate for MUS? Around the world, the trend is toward irrigation with increasingly lower quality water. When are benefits of increased quantity of water for domestic uses exhausted by negative effects of lower quality? Health concerns for direct ingestion as well as indirect exposure to pathogens through food Existing WW standards address latter issues but not former Suggests the need for a more complex institutional/ regulatory framework to protect public health Davis 2006 Significance of this debate for MUS? Ensuring adequate supplies of potable drinking water within a MUS framework Investment in potable water storage infrastructure (e.g., rainwater harvesting) Household-level water treatment (“point of use”) Davis 2006 Significance of this debate for MUS? Point-of-use water treatment for microbial contamination Physical processes (heat): boiling, thermal disinfection, UV disinfection Physical processes (particle removal): filtration (sand, ceramic, sari cloth, etc.), coagulation, flocculation (alum, iron hydroxides), settling Chemical disinfection: chlorine, iodine Challenges for sustainability (e.g., continued protocol compliance, supply chains, O&M) and for equity (e.g., affordability of access) Davis 2006 Significance of this debate for MUS? Water quality: “reality” vs. perception Eastern Islands, Indonesia: Functional piped systems unused because of local responses to chlorine Manila, Philippines: ~40% of HHs using ‘protected sources’ regularly treating water (boiling & filtering) California: ~70% of HHs rely principally on bottled or filtered water for drinking in the home Davis 2006 Conclusions In both irrigation and W&S service literatures, evidence from users that bifurcated planning produces outcomes that fail to meet users’ needs MUS approaches may create, reduce, or have no effect on W&S-related health problems Current treatment of W&S-related health concerns in MUS literature appears limited
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