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CHAPTER 2.2 DOMESTIC WATER AND SANITATION


require local faecal sludge management (that is, excreta removal and treatment). Excreta management is gender-segregated and often racially differentiated. A 2014 Human Rights Watch report on the caste and gender profile of manual excreta cleaners in India revealed that 95% of private and village latrines were cleaned by women; both women and men cleaned open defecation from roads, open areas and open gutters, while men typically cleaned septic tanks, closed gutters and sewers (Human Rights Watch 2014).


There are recent trends towards the development of environmentally sustainable sanitation systems, which are increasingly under consideration as feasible and affordable alternatives for rural municipalities, low- income small communities or groups of households (Wendland and Albold 2010). These systems range from natural approaches such as the use of ponds and constructed wetlands (which are low-tech and low- maintenance) as filters and for cleaning wastewater, to high-tech vacuum biogas installations. Bacterial contamination from faeces can be broken down quickly in natural systems such as wetlands and planted soil filters.


Modern on-site sanitation systems that allow the reuse of nutrients and organic matter present in human excreta, as recommended by WHO (2006), are also being developed as alternatives to septic tanks and individual


household systems. Retrieving nutrients


from human and animal waste, at source, for reuse has received increasing attention in recent years (Schröder et al. 2010). “Productive sanitation” is the overall term for sanitation systems that focus on increased crop yields by using treated excreta and grey water in agriculture. The gendered dimensions of productive sanitation projects have not yet been fully explored, although some aspects are already apparent (Wendland et al. 2012).


In terms of impact, women would benefit directly from the increased availability of nutrients that can be used for rural and urban agriculture (Hannan and Andersson 2002). For example, the urine diversion dehydration toilet requires no water for flushing, reducing the workload of women if they have to fetch water for sanitation (Wendland et al. 2011). In Zimbabwe women in some rural areas have indicated they prefer an ecological sanitation alternative that can be built closer to their homes (the “Arborloo”) than conventional pit latrines. When Arborloo pits are full,


women plant fruit trees in them; men also prefer an Arborloo since the pits are shallower and require less work to dig (Wendland et al. 2012).


The disposal of ready-made sanitary pads – which contain significant amounts of plastic – could be another threat to human health, rural and urban environments, and social relations. It requires not only a proper sanitary disposal system, but also awareness- raising programmes (particularly in rural areas) on safe disposal methods and available alternative technologies. Waste management strategies need to give adequate consideration to MHM (SSWM 2016; House et al. 2012; Ten 2007).


The “missing half”: the need for gender-disaggregated data on water and sanitation


One of the worst stumbling blocks in regard to achieving


a more robust gender-integrated


international policy regime is lack of comparable international data on gender-sensitive water and sanitation indicators. International policy mechanisms are driven by data. Without gender-disaggregated data it is impossible to fully measure progress towards sustainable development goals, or to make effective analytical assessments of the comparative situations of women and men in different communities or parts of the world (UN DESA and UNW-DPC 2009). The Gender and Water Alliance has identified gender- disaggregated data collection as a key component of a “minimum agenda” for making a difference in water management (GWA 2006). The International Fund for Agricultural Development (IFAD) has also identified the “unavailability of gender-disaggregated data” as one of the main reasons for the gap between policy commitments on water and gender and actual practice (IFAD 2007).


In 2013 the United Nations Economic and Social Council (ECOSOC) reported on the state of gender statistics across the UN system and across national platforms. Gender-disaggregated water and sanitation statistics were among those that were least available (Table 2.2.3).


A study prepared for the World Water Assessment Programme (WWAP) shows the gender focus in major international data compilations is actually declining


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