INVESTMENT NOTE 10.1 GENDER, PARTICIPATION AND DECENTRALIZATION IN AGRICULTURAL WATER MANAGEMENT The user target group for agricultural water management investment projects is highly diverse: women and men, landowners and tenants, and communities cultivating communal land without clear ownership title. Taking this diversity into account through inclusive participatory project design and implementation is critical for poverty alleviation, gender equity, and water productivity, especially in female and dual farming systems. Membership of Water Users Associations should include all the user groups. A more recently recognized form of diversity relates to multiple water uses and the need for water for both productive and domestic water uses. INVESTMENT AREA The target group of agricultural water development, management and protection projects is highly diverse and extends far beyond the traditionally assumed target group of male farm household heads who own land, and represent a supposedly-unitary household where all resources and benefits are pooled and then shared equitably. This diversity exists also among poor water users who face constraints to voicing their needs due to: misconceptions about the intrahousehold organization of farming; land tenure arrangements especially where communal land and tenancy forms prevail; and non-agricultural water needs. Firstly, diversity exists in the intra-household organization of farming (male-; female- and dual- farming systems)1 particularly relating to who makes decisions on farming. This depends on both the local prevailing farming system and household-specific characteristics such as male outmigration; disability; or other capacity issues. Diversity thus exists in the tenure arrangements of farm decision-makers, including, for example, entitlements to land and water resources for crop cultivation and other uses. Thirdly, diversity exists in water needs in poor rural areas where household livelihoods are diversified and water-dependent. For example, women and men use water for domestic purposes; cropping; gardening; livestock; fisheries; trees and nurseries; and small enterprises. Recognition of this diversity is critical for pro-poor and gender-equitable design and implementation of agricultural water investments. Key questions in the design process include: Who is the target? Whose land is to be improved? Who should be allocated newly-developed irrigation plots? What membership criteria including gender quotas, should be set for new Water Users Associations (WUAs) during Irrigation Management Transfer? How much water should be 1 Van Koppen drawing on Safiliou 1988 has categorized farming systems as: male-; femaleor dual-farming systems according to whether farm decision-makers are predominantly male or female, or both (with the gender division of labor depending on such factors as land tenure; and male out-migration). reserved for uses other than field crop irrigation? Women agricultural producers are also a diverse group: laborers, independent farm decision-makers and traders. Although many projects assume a benevolent ‘unitary household model’, research indicates that intra-household organization of farming can be understood best as a ‘bargaining model’ where household members negotiate implicitly with each other to secure resources for their own production subunit, from their different – and often hierarchical bargaining positions (Quisumbing 1996; Haddad 1997). Further, bargaining power is asymmetrically allocated. The resulting ‘gender yield differential’ has been calculated by Udry et al (1995) who examined plot-level agronomic data in Burkina Faso for households where men and women controlled different plots but were raising the same crop. Due to prevailing gender relations, inputs of labor, manure, and fertilizer were applied with differential intensity (with men’s plots receiving more inputs), resulting in reduced overall household input and allocative inefficiency in that resources were neither pooled nor traded among household members. The production function in this study estimated that with a reallocation of these factors of production between men’s and women’s plots, household output could be increased overall by 1020 percent (ibid). As noted above, different production sub-units are managed by different adult members. Household horticulture; livestock; irrigated plots; and small enterprises tend to be typically managed by either men or by women in particular farming systems, according to longestablished practices and traditions (Safiliou 1988). These areas of control are dynamic and can respond quickly to changes in opportunities and incentive structures, whether due to market forces such as the development of alternative employment and income sources; or project-based incentives such as targeting of extension services or other inputs to women; or new assets such as collectively-held infrastructure or resources providing, for example, fruit nurseries organized by women’s cooperatives. In addition, land ownership and de facto farm decision-making need not coincide as, for example, the (male) land owner may be absent; or women farmers may cultivate the land of their male in-laws. In Asia and among the poor, the actual water user is often a tenant or sharecropper without land title. Alternatively, land tenure may be communally-held, without a single owner. Such tenure arrangements must be considered in the project design and targeting, as well as in WUA membership criteria in order to reduce the possibility of social exclusion. Finally, rural people’s water needs are diverse. This is clear from the universal observation that whether planned or not, publicly supported ‘irrigation’ water is typically used for many purposes other than irrigation, such as domestic uses and livestock. Such unplanned uses are equally observed in publicly-supported domestic water schemes. The dichotomy between water for ‘domestic’ and ‘productive’ purposes according to sector-based structuring of the water sector, fails to fit the reality of people’s needs. While it is well recognized that 2 women are engaged in obtaining water for domestic and productive uses, men also contribute to domestic water provision for the health of their families. Recognizing women’s and men’s multiple water needs opens up new investment opportunities for synergistic multiple-use water services. POTENTIAL BENEFITS Taking into account the diversity among the target group is crucial for the project's efficiency and its impact on reducing poverty. Gender-sensitive design and implementation of agricultural water development and management projects, including the creation of inclusive criteria for WUAs, is a matter of gender equity and a necessary condition for the project to reach its productivity goals (see Box 10.1.1). This is especially the case in those areas or those farming types where approximately half the farm decision-makers are women (that is, in dual farming systems) and even more crucial where women form the majority of farm decision-makers (see Box 10.1.2). Increased and improved attention to gender in agricultural projects in Africa, in particular, is likely to translate into immediate productivity gains, due to the region’s high ‘gender intensity of production’ with women providing 80 per cent of the food crop and non-traditional agricultural export labor force ( Blackden and Bhanu, 1999). Strengthening women’s land and water tenure security, and access to agricultural inputs and markets, encourages women farmers to make long-term investments in land-bound water technologies. This is pivotal for agricultural growth in general. Box 10.1.1 GENDER, PRODUCTIVITY, AND WETLAND IMPROVEMENT IN BURKINA FASO Women farmers are as productive as men farmers, provided they have equal access to resources and inputs, and control their agricultural outputs (Quisumbing 1997). In female farming systems of wetlands in south west Burkina Faso, gender-sensitivity in the project design appeared the single most important success factor for a rice project that improved infrastructure and agronomic practices. Initially, the improved plots were allocated to ‘male heads of households’, while women were supposed to continue providing all the labor. Women were also excluded from the Water Users Associations because membership was vested in the land owner. Without their customary control over the output, women lost their motivation to cultivate. Men generally failed to fulfill their infrastructure maintenance obligations. And this led to infrastructure decline and even partial abandonment of the ‘improved’ schemes. In later schemes, the allocation procedures changed at the initiative of women plot holders, their male kin, and male and female land chiefs. New plots were allocated first to existing plot holders. Men were explicitly invited to apply for new rice plots. Women, however, were the majority of new applicants. Membership was vested in the farm decision-makers. Women fulfilled their obligations of infrastructure maintenance work and reaped the benefits. Source: Van Koppen 2000. In male farming systems as found in northern Europe and South Asia, women generally work as unpaid family laborers, and are excluded from farm decision-making. To enhance gender equity in these systems requires addressing more deep-rooted gender discrimination. Agricultural marketing cooperatives for women, such as those 3 sponsored by SEWA (http://sewa.org) in India, may be a highly effective way for women to undertake their own income generating activities. The Uttar Pradesh Sodic Lands II Project in India also found credit self-help groups for women farmers to be highly effective as a project intervention, especially when complemented by separate men’s and women’s water user groups at subvillage level (Kuriakose et al 2005). Irrigation development projects often include land titling components. In addition, these projects can recognise and support women who are sole farm decision-makers as heads of households and who have to contribute labor inputs to meet land reclamation or maintenance requirements. The labor contribution is especially important as this is often the basis for acquiring land or water rights. Women may also be excluded from WUA membership and the opportunities for effective participation and leadership and they may have limited access to agricultural extension. If seclusion norms limit a public role for women or even contact with non-family or non-local persons, especially if male, it is important that the project design ensures that female extension agents are on the staff of irrigation and agricultural agencies. Box 10.1.2 SYSTEMS GENDER AND FARMING Female and dual farming systems are widespread in southern and eastern Africa where 50 - and in some districts up to - 90 percent of the farms are female managed. This is due to off-farm employment opportunities and male outmigration, and to a long-standing cultural division of farming activities in which livestock keeping tends to be managed by men, while cropping is managed by women (Safiliou 1994). Rice cultivation in wetlands in western Africa is another example, where women are often the majority of farm decision-makers (Van Koppen 2000). In Asia too, there are areas where women constitute the majority of farm decision-makers, as in Nepal. (Zwarteveen and Neupane 1996). Box 10.1.3 TENANCY, SOCIO-SPATIAL EXCLUSION AND WUA MEMBERSHIP In Punjab, Pakistan tenants’ rights to join farmer organizations (FO) vary depending on the nature of the tenancy arrangement. More ‘permanent’ tenants long associated with a certain plot of land are often delegated the right to organizational membership, though this remains the prerogative of the landlord, and is thus vulnerable to manipulation. Tenants whose arrangements vary more often (for example, annually) abstain from joining the FO as it is considered a long-term institutional arrangement incompatible with their rapid tenure turnover Spatial settlement patterns also matter for inclusion in FOs. In Punjab, residents of one ‘additional settlement’ on the outskirts of the main village were forced to organize their own formal FO when they were not permitted by main village farmers to join that organization. The new FO then forced the main village FO to allocate water fairly between the two parts of the village. Source: Kuriakose et al Forthcoming. Recognizing and responding to the multiple forms of land tenure and titling arrangements in farming systems helps ensure that the project design supports actual farm decision-makers (including women and tenants) rather than absentee landowners or male kin who may have fewer interests in agricultural production and irrigation scheme operation and maintenance (see Box 10.1.3). The starting point for water project design is support for multiple-use water services that take into account total 4 needs of water users. This is especially important for women and the poor who depend more upon public investments than wealthier farmers. For the poor, the unplanned use of ‘irrigation’ water for fisheries and livestock is also particularly important. For women, domestic uses of ‘irrigation’ water have often been the major benefit of ‘irrigation’ projects. Water management planning based on multiple needs has proven to have many benefits that are pro-poor and gender-equitable and generate: Improved Well-being in Areas of food, income, and health. Multi-use systems are gender-friendly by design as domestic uses are recognized as a priority use, even in ‘irrigation’ settings. They address health issues holistically, aiming at incremental improvements in access to water for drinking. Such an approach acknowledges that access to more water has important hygiene and health effects, especially when combined with point-of-use water treatment to improve water quality for drinking whether as part of formal drinking water supply projects or in more generic water delivery projects. Improved Sustainability and Ownership through: higher willingness to pay for services that better meet people’s needs, especially when compared to ‘domestic-only’ schemes; strengthened ability to pay; stronger ownership by communities, who have long been designing their own means of water management for multiple purposes; avoidance of damage to the system, common when single-use systems are used for multiple purposes in an unplanned fashion (for example, erosion from livestock uses); more equitable and efficient impact by ensuring that poor people’s domestic and productive basic water needs are met; and higher water productivity through optimal use of the resource. Modest Incremental Cost, though Attention to Management Issues is Required. The basic water technologies (storage, lifting, conveyance, and drainage) for multiple water uses are similar to single-use schemes and , the way in which these technology components are assembled allows for water use for various purposes. In this way, incremental costs for multiple-use technologies may be low. However, management issues may be complex, involving participatory and needsbased water planning and allocation and other trade-offs, particularly between reserving water for daily domestic and livestock uses, versus allocating water for crop irrigation purposes with rotational and seasonbased delivery. Differences among uses in water delivery timing and duration, quantity, and quality need to be taken into account for multipleuse management. However, one integrated Water User Association avoids parallel committees for ‘domestic’ uses, ‘irrigation’ and so on, for the same water resources used by the same households. Multiple government departments are also involved and have to address such issues as water quality that arise in multiple-water use planning environments. 5 At the plot or household level: Designing water supply to meet women’s and men’s productive and domestic uses (for example, home gardening by women; no night turns or distributions in irrigation schemes; joint titling of irrigated land). At the project level: Designing special elements in ‘irrigation’ schemes such as washing steps for laundry use; cattle entry points for livestock watering; year-round reservoirs for cattle and domestic uses and providing year-round availability for such uses. At the community or collective level: Including women and men in multipurpose WUAs (including all water uses); vesting membership in all water users, and for agricultural water use: vesting membership with the farm decision-maker, irrespective of gender and type of land tenure; ensuring convenient timings of meeting, transport, and venues; and establishing transparent and open procedures in WUA meetings. At the local-leadership level: Including women and the poor in decision-making bodies, such as WUA committees. In setting quotas, gender composition should, at a minimum, reflect the actual proportion of women and men farmers. Leaders from marginalized groups need to be supported and trained in their new roles (see Box10.1.4). POLICY AND IMPLEMENTATION Box 10.1.4 GENDER MAINSTREAMING IN PROJECT IMPLEMENTATION Inclusive water users association (WUA) membership criteria have been developed as part of the Maharashtra Water Sector Improvement Project in India, approved by the Bank’s Board in 2005. In line with the State Irrigation Act 2005, WUAs in the project are mandated to have women members as part of the general body and executive committee. Gender and tribal strategies exist for the project, following a comprehensive social assessment undertaken for the project on gender, tribal and other issues. Additionally, an Environment and Social Development Sub-Unit within the project has been set up to help ensure that social objectives are achieved. Such attention to gender and social vulnerability within the project cycle and project implementation mechanisms is expected to yield good results on both social and economic outcomes. Source: World Bank Maharashtra Water Sector Improvement Project. P084790. Project Appraisal Document. 2005. Implications for gender; land tenure forms; and multiple water needs should be assessed and considered from the beginning of the project in order to design holistically for women’s and men’s domestic and productive water needs. This can best be done through participatory project planning and implementation to prevent elite capture of the benefits of the project and allow for project beneficiaries or their representatives to effectively voice their needs, preferences, opportunities, and constraints. Such participatory planning requires resources and can imply the following: Box 10.1.5 SOCIO-ECONOMIC STRATIFICATION AND ACCESS TO WATER FOR LIVESTOCK WATERING 6 An International Water Management Institute study in Pakistan found that socio-economic level affected households’ access to water for livestock watering. Better-off households living on larger farms were able to keep their animals in stalls on their home compound bathing and watering the animals with the same domestic water the family used (that is, groundwater from hand pumps, motor pumps and wells). Ninetyfive percent of respondents from such households found water sources sufficient for their animals. In contrast, poorer households (and those few households who lived near their fields further from the village) had to drive their animals to canal watercourses and distributaries for watering and bathing. Only 71 per cent of such respondents found these water access arrangements satisfactory. Further, livestock use of canal water is illegal and pollutes the distributary water for downstream domestic users. Notably, the traditional livestock pond held in common in each village is now being degraded by release of waste water and sewage by those households with private sources of water . ‘irrigation’ sector can broaden its objectives in a similar way. This may lead to improved sustainability of systems. In female and dual farming systems, gender-sensitive project design is a particularly important route to achieving water productivity and gender equity. In male farming systems, varied interventions are required given prevailing gender norms. Here separate women’s organizations can be highly effective. Land ownership as a membership criterion for WUAs tends to exclude poor and female farmers holding secondary tenancy; intra-household; or communal land rights. Such exclusion of water users can jeopardize the functioning of the association. Quota systems are an effective way of ensuring representation for women’s interests in water decisionmaking organizations. Source: Kuriakose et al Forthcoming. LESSONS LEARNED Women and men; adults and children; agriculturalists; pastoralists; fishermen and women; or small scale entrepreneurs have different, multiple water needs, due to their diversified livelihoods. The opportunities to meet these unmet water needs through multiple-use water services provision are still largely untapped ( see Box10.1.5). For women and the poor, the nonirrigation uses of ‘irrigation’ water are often a priority. While WUAs rarely include all water users, the domestic water sector increasingly initiates water supply provisions that take poor people’s multiple water needs as the starting point. The RECOMMENDATIONS FOR PRACTITIONERS Provide for target group diversity with an open, inclusive and needsbased design of the project without a priori assumptions about people’s water needs, and which enables the target group to articulate its needs. Base gender-sensitive design on women’s and men’s multiple water needs; on a sound understanding of the gender role in the farming system; and on targeting women 7 farm decision-makers on the same basis as men farm decision-makers, at farm level, at community and collective level, and in leadership positions. Ensure inclusive WUA membership criteria, irrespective of gender and type of land titles Set quotas in WUAs to ensure that leadership composition reflects, at least, the gender division among farmer members, and that general representation reflects equal gender composition. INVESTMENT OPPORTUNITIES Water development and management projects with participatory and inclusive planning and design, should provide for multiple water needs, especially of poor women and men and include low-cost infrastructure for multiple uses; and financing earmarked for multiple-use application. Support capacity-building for members of marginalized groups and women to participate as members and leaders in WUAs. Support capacity-building in water agencies to improve analytical skills among staff; and to provide skills to assess and to develop pro-poor and gender-responsive agricultural water management policies. Support the recruitment of female extension agents to sector agencies, and the targeting of female farmers in the delivery of agricultural services . REFERENCES CITED Bakker, Margaretha, Randolph Barker, Ruth S. Meinzen-Dick and Flemming Konradsen. 1999. Multiple Uses of Water in Irrigated Areas: A Case Study from Sri Lanka. SWIM Report 8. Colombo, Sri Lanka: International Water Management Institute . Blackden, Mark and C. Bhanu. 1999. Gender, Growth and Poverty Reduction: Special Program of Assistance for Africa – Status Report on Poverty in SubSaharan Africa. Washington DC.:. World Bank Haddad, L., J. Hoddinott, and H. Alderman (eds). 1997. Intra-household Resource Allocation in Developing Countries: Methods, Models and Policy. Baltimore: John Hopkins University Press for the International Food Policy and Research Institute Kuriakose, Anne T., Waqar A. Jehangir, and Mehmood ul-Hassan. Forthcoming. “Will the Diggi Go Dry? Multiple Uses of Irrigation Water in Punjab.” Pakistan. Society and Natural Resources. Kuriakose, Anne T. et al. 2005. “Gender Mainstreaming in Water Resources Management.” ARD Internal Paper. Washington DC: World Bank. Quisumbing, Agnes. 1996. “MaleFemale Differences in Agricultural Productivity: Methodological Issues and Empirical Evidence.” World Development. Vol. 24. No. 10. pp 15791595. Great Britain: Elsevier Science Ltd 8 Safiliou, Constantina. 1988. “Farming Systems and Gender Issues: Implications for Agricultural Training and Projects.” Unpublished paper. Ministry of Agriculture and Fisheries of the Netherlands and the International Agricultural Centre. Wageningen Safiliou, Constantina. 1994 “Agricultural Policies and Women Producers.” In Gender, Work and Population in Sub-Saharan Africa, ed. Aderanti Adepoju and Christine Oppong, International Labour Organization. London: James Currey and Heinemann Udry, Christopher, D. Hoddinott, H. Alderman, and L. Haddad. 1995. “Gender Differentials in Farm Productivity: Implications for Household Efficiency and Agricultural Policy.” Food Policy. 20(5). Van Koppen, Barbara. 2000 “Wetland Improvement in Burkina Faso.” In Negotiating Water Rights, Bryan Bruns and Ruth Meinzen-Dick. India: SAGE WORLD BANK DISCUSSED Merrey, Douglas J., and Shirish Baviskar (eds). 1998. Gender Analysis and Reform of Irrigation Management: Concepts, Cases and Gaps in Knowledge. Proceedings of the Workshop on Gender and Water. September 1997. Colombo, Sri Lanka: International Water Management Institute Van Koppen, Barbara. 2002. “A Gender Performance Indicator for Irrigation. Concepts, Tools, and Applications.” Research Report 59. Colombo: Sri Lanka: International Water Management Institute Van Koppen, Barbara, Patrick Moriarty, and Eline Boelee. 2006. “Multiple-Use Water Services to Advance the Millennium Development Goals.” Research Report 98. International Water Management Institute. Colombo, Sri Lanka: International Water Management Institute. This Note was prepared by Barbara van Koppen of IWMI and Anne T. Kuriakose, and reviewed by Ruth Meinzen-Dick of IFPRI and Eija Pehu. PROJECTS India. “Uttar Pradesh Sodic Lands Reclamation Project II”. Active. Project ID: P050646. Approved: 1998. India. “Maharashtra Water Sector Improvement Project”. Active. Project ID: P084790. Approved: 2005. SELECTED READING 9