1 Socio-technical aspects of water management: the case of Water Users Associations 2 (WUAs) in Uzbekistan 3 Iskandar Abdullaev- Senior Researcher, Center for Development Studies, Bonn, Germany, e- 4 mail: i.abdullaev@uni-bonn.de 5 Peter Mollinga- Senior Researcher, Center for Development Studies, Bonn, Germany, e-mail: 6 pmollinga@uni-bonn.de 7 Ahmad Manschadi- Senior Researcher, Center for Development Studies, Bonn, Germany, e- 8 mail: manschadi@uni-bonn.de 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 1 26 Socio-technical aspects of water management: the case of Water Users Associations 27 (WUAs) in Uzbekistan 28 Abstract 29 This paper describes a socio-technical framework to assess irrigation water management systems 30 in the Central Asian state of Uzbekistan. The framework builds on the boundary concept “water 31 control” for analyzing water management at the meso and regional levels in a (semi- 32 )authoritarian context. In Soviet times water management was generally considered as a 33 technical issue (to be) taken care of by the state water bureaucracy. Due to structural changes in 34 agriculture in the two post-independence decades, irrigation water management has become a 35 political and social issue in Central Asia. 36 With the state still heavily present in the regulation of agricultural production, the situation in 37 Uzbekistan differs from other post communist states. The water management strategies are still 38 strongly ‘soviet’ in approach, being regarded by state actors as purely ‘technical’, because the 39 other dimensions, economic, social and political, are ‘fixed’, through strong state regulation. 40 However, new mechanisms are appearing in this authoritarian and technocratic framework. 41 The socio-technical analysis framework was applied in some selected Water Users Associations 42 (WUAs) in northwest Uzbekistan, Khorezm region. The WUAs are becoming arenas of 43 interaction for different actors involved in water management. Results of this study help to 44 understand changes in water management and their possible consequences for livelihoods of 45 different rural groups, highlight water management problems of the study area, and determine 46 future research questions. The methodology tested in the Khorezm region is applicable to other 47 areas of rural Uzbekistan and irrigated landscapes of Central Asia where more or less (semi-) 48 authoritarian policy frameworks apply to agriculture. 49 The socio-technical analysis of Khorezm water management highlights growing social 50 differences at grass root level in the study Water Uses Associations. The process of social 51 differentiation is in its early phases and is still to express itself fully due to strict state control of 52 agriculture and social life in general. 53 54 55 Key words: water management, socio-technical, water control, Uzbekistan, state quota 2 56 Introduction 57 Societal problems are multi-faceted and complex. For instance, natural resources management 58 (NRM) has several components and dimensions that influence each other. The solution to NRM 59 problems requires an understanding of both natural resources systems and their interactions with 60 human (management) systems (Mollinga, 2009). Multi- dimensional societal problems require 61 changing the “business as usual” approach on NRM research, especially on water resources 62 management. The response to growing NRM problems, particularly in the water sector of the 63 Central Asia has been one of “normal professionalism” (Chambers, 1988) of water sector 64 researchers and engineers. “Normal professionalism” is a standard, disciplinary, limited response 65 to problems, which is reproduced in the education system. This has contributed to the 66 reproduction and continuation of problems and has been generating limited approaches for 67 addressing water management problems. 68 Characteristics of an inter- and transdiciplinary approach to complex water resources 69 management problems are the following. (1) acknowledges the complexity and heterogeneity of 70 problems and organizations, , (2) accepts local context and uncertainty, (3) implies interactive 71 action and is inter-subjective, (4) is in most cases action oriented, making linkages across 72 disciplinary boundaries (Mollinga, 2008). 73 This is especially relevant for Central Asia, where water management in the past decades has 74 changed from a centralized, purely technical issue to a debated and contested transboundary, 75 socio- political endeavor (Dukhovniy. 2008, Abdullaev. 2000, Abdullaev et al. 2009). The 76 disciplinary and government-directed research efforts from the Soviet period do no longer suffice 77 for improving water management in modern Central Asia. The old approach no longer applies 78 for the following reasons: 79 1. Due to the major geopolitical change of the collapse of Soviet Union, both governance and 80 management of transboundary water resources between five countries became more of a political 81 process. During Soviet times water management was regarded as purely ‘technical’; the other 82 dimensions were under strict control from a central point, Moscow, and in this sense given and 83 unchangeable. With five sovereign states sharing the central Asian rivers, a new politics has 84 emerged. 85 2. Post – soviet changes in agricultural policies have brought very serious social changes in rural 86 areas. The ensuing social differentiation of the rural population has been captured by different 3 87 research studies (Kandiyoti, 2003, Trevisani, 2008). Therefore, previous research on water 88 management when collective farms were the main agricultural producers became irrelevant for 89 today. The community of water users has become internally differentiated through the 90 emergence of larger and smaller farms 91 3. The environmental consequences of the previous “hydraulic mission” (Allan, 2006) have been 92 catastrophic for the region (Abdullaev et al., 2009). Therefore, research that speaks to a series of 93 problems and concerns, including ecology, equity, and governance, beyond the concept of 94 ‘development’ in the earlier soviet sense, is needed. 95 This paper presents a framework for socio-technical1 analysis of water management and results 96 of its application in the Khorezm region, Uzbekistan2. The main element of the framework is the 97 boundary concept3 “water control” (Mollinga. 2003, 2008) which was applied to capture three 98 interlinked processes in water control: physical, organizational and socio-economic/political. 99 Research framework and methodology 100 Research Location 101 The Khorezm region in Uzbekistan is biophysically representative for the irrigated Amu Darya 102 lowlands of Central Asia, which comprise the entire irrigated land (1 060 000 ha) between the 103 Tuyamuyun reservoir and the Aral Sea (figure 1). The region well represents those of post- 104 independence changes in agriculture. Since 1991, in place of only few hundred collective 105 thousands of private farms were organized. The total irrigated area accounts for about 10% of the 106 entire Aral Sea Basin (ASB). The total population 1.3 million people living in Khorezm, about 107 70% are rural and about 27.5% live below the poverty line (1 US$ per day); unemployment rates 108 especially in rural areas, are high (Mueller at al. 2007). 1 Socio-technical analysis was borrowed from Mollinga (2003) for describing two interlinked parts of water management systems: the first is infrastructure and the second is the human factor in managing water. 2 This research has been conducted within the framework of the BMBF (German Ministry of Education and Research) funded project Economic and Ecological Restructuring of Land- and Water Use in the Region Khorezm (Uzbekistan): A Pilot Project in Development Research. 3 “Boundary concepts are words that operate as concepts in different disciplines, refer to the same object, phenomenon, process or quality of these, but carry different meanings in those different disciplines” (Mollinga. 2008) 4 109 110 Figure 1. Khorezm region- location of study area (Source: Martius et al. 2008) 111 Research Framework 112 Socio-technical study of water management was conducted within the framework of the water 113 studies of German-Uzbek project in northern Uzbekistan”4. The objective of the work package 114 on water management is “to consolidate and adapt the framework for socio-technical analysis of 115 water management, intensive application of this framework for studying of field-farm, WUA and 116 main system level irrigation management practices, identification of options and approaches on 117 restructure of existing water management towards IWRM, developing suggestions of innovations 118 on irrigation and drainage management in close consultation with network of stakeholders 119 (agricultural producers, WUA officer bearers and relevant government officials), close 120 monitoring of the evolution of the drainage and irrigation management approaches at the 121 provincial (Khorazm) , national (Uzbekistan) and regional (Central Asia) levels”5. “This project specifically aims at providing a comprehensive, science-based, plan for restructuring at three nested intervention levels: policies, institutions, and technologies” (Economic and Ecological Restructuring of Land- and Water Use in the Region Khorezm (Uzbekistan). A Pilot Project in Development (Martius et al. 2006. Research Proposal for Project Phase III: Change – Oriented Research for Sustainable Innovation in Land and Water Use (2007-2010)) 4 5 Operational Work plan for work package 320 - Integrated Water Resource Management (IWRM) for Khorezm: BUIS-, WUA and farm-level operation of I&D system in practice (Abdullaev.2008) 5 122 The objective of the work package requires systematic research on understanding and developing 123 Integrated Water Resources Management (IWRM) approaches for improvement of water 124 management in close consultation with stakeholders. This requires an inter- and transdiciplinary 125 research, because the main target is to address the societal problem of water management and 126 this requires great degree of care about local context, action oriented research with contribution 127 to the solution of the problem (Mollinga. 2008). 128 The socio-technical research includes three dimension of water management (physical, 129 organizational and socio-economic-political) and links these with different spheres of water 130 management: physical shape of irrigation – drainage system, institutions and organizations and 131 social structure- governance. A range of research methodologies such as surveys, measurements, 132 data collection, institutional analysis are applied within framework for socio-technical analysis 133 (figure 2). 134 135 Figure 2. Research Framework and methodology for socio-technical analysis of water 136 management 137 The research framework described above was applied to the everyday politics of water 138 management in the study sites in Khorezm province, Uzbekistan. 139 water management refers to the interactions of different groups on planning, distribution and use 140 of water on a daily basis, and looks at these as a process of contestation. 141 The central issues of everyday politics looked in this research were: 6 The everyday politics of 142 the concept of hydraulic property The new arrangements made for operation, use and 143 maintenance of the irrigation and drainage infrastructure pre-determines water control 144 strategies of the different groups; 145 the understanding of collective action. Changing agricultural production systems from 146 collective to individual production has made irrigation and drainage network ownership and 147 use rights a very central issue of water control. Analysis of the collective action process helps 148 to understand how different actors are strategically engaged with each other in the arena of 149 the everyday politics of Khorezm water management? 150 The everyday politics of water management is understood through application of Long’s actor- 151 oriented approach (Long, 2001). Long (2001)’s actor-oriented approach to study social behavior 152 and interaction is based” upon the capacity of actors to process their and others experiences and 153 act upon them”. For capturing the processes of water control it is very important to select 154 specific locales or sites where the everyday politics can be concretely observed. The 155 transformations in agriculture and water sector in Uzbekistan after 1990 (Yalcin and Mollinga. 156 2007, Trevisani. 2008, Wall. 2006) have created new interfaces or discontinuities in water 157 management. The processes that have generated these are the restructuring of the collective 158 farms into smaller units, and the establishment of new organizations like Water Users 159 Associations (WUAs). WUAs have been created at the former collective farm level in the last 160 decade. The uniqueness of WUAs is that they are located at the level where the state meets with 161 water users (Veldwisch, 2008; Abdullaev et al., 2008). Four specific interfaces could be 162 identified at WUA level: local government-WUA, water management organizations (WMO) - 163 WUA, WUA-water users (farmers) and water users –water users (figure 3). 164 7 165 166 Figure 3. Four interfaces in the everyday politics of WUA water resources management 167 The interface 1 represents everyday interactions between local government officials (in local 168 hakimyat) and Water Users Association (WUA). The WUA management are attending to the 169 regular meetings with local government officials. 170 implementing decisions made by government on agriculture and on water management 171 (Wegerich. 2000, Zavgordnyaya. 2006). This interface is therefore understood as relationship 172 between higher and lower hierarchical levels, therefore in figure 2 arrows coming from hakimyat 173 are bold, arrows from WUA is thin. Because role of WUA in this interface is more of subsidiary 174 and secondary: providing information and accepting tasks from hakimyat. In the case study area 175 this interface is described how a state quota and water turns (asvak) are implemented. 176 The interface 2 is daily interactions between WMO and WUA. It is similar to the interface 1 but 177 more of professional interaction. WMO are preparing and controlling water use plans for WUA. 178 They are also playing the role of arbiters on water related conflicts between different WUAs and 179 between WUA and individual farmers. The ownership of most of the water infrastructure makes 180 WMO in interface -2 more leading. However, WMO does not have as strong control over WUA 181 as hakimyat have. The interaction between WMO and WUA in the case study is illustrated 182 through water turn- asvak implementation. 183 Interface 3 represents interaction between water users (farmer) and WUA. This interaction is at 184 the core of everyday water management. WUA is on one hand trying to implement decisions of 185 local hakimyat and WMO and on the other hand tries to manage water between different farmers 8 In Uzbekistan WUAs are still used for 186 (cotton-wheat6, commercial) and other water users. In this interface different water users apply 187 technical, social and political water control strategies for access to water resources (Veldwisch. 188 2008). Interface 4 represents interaction between different groups of farmers, between farmers 189 and smallholder land owners and non-irrigation water users. 190 Actors7 involved in the everyday politics of water management could be divided into four 191 groups: (i) water users, (ii) state bodies, (iii) irrigation and drainage infrastructure, (iv) social 192 and natural environment (figure 4). Although this categorization of the actors is helpful, it does 193 not present the heterogeneity within each group, e.g. in one water users group there are different 194 water uses and users with different water consumption patterns (figure 4). 195 196 Figure 4. Main actors of everyday water management 197 It is important to note that in this research human and non- human actors are treated 198 symmetrically. Actions and water control strategies of human actors are shaped by the social and 199 natural environment and by irrigation and drainage infrastructure, state policies and regulations. 6 State quota for cotton and wheat means that the state through its semi- state organizations will sign agreements with individual farmers for delivering pre-determined amounts of wheat and cotton. The farmers who are assigned by local government (hakimyat) to grow cotton and wheat should follow strict rules of growing cotton- wheat: agro technical (when to do sowing, irrigation, fertilization, etc.), land use (where and how many hectares of which crop to be sown) and administrative (attending to daily meetings, obeying state authority, etc.). The plan for state quota is determined by the local government (hakimyat) using land quality (bonitet) grades of the piece of farmland. 7 Actors as used in this paper are taken from actor- network theory (Latour, 1987). Actor Network Theory tends to speak, in French, of ‘acteurs’ (human actors), and ‘actants’ (non-human actors). Both human and non-human actors play a role in everyday water management– even when these roles are different. 9 200 Therefore, in this socio-technical research authors do not allocate any pre-determined weight to 201 any of the actors. 202 Research Methodologies and Techniques 203 As indicated in section on research framework WUA is essential arena where different interfaces 204 on everyday water management happen. Therefore, in this research WUA has been a central 205 focus area for socio-technical analysis of water management. Five WUAs, located in different 206 biophysical, social and institutional conditions were selected with aim to get a diverse set of case 207 studies (Abdullaev et al., 2008). In this paper authors will present results of socio- technical 208 analysis in one study WUA. 209 The field research consisted of exploratory and documentary methods. These included semi- 210 directive, un /semi structured and group interviews with main actors, studying of project reports, 211 data bases, research publications, archives and mass-media materials on both subject and area of 212 interest. For observation of the non-human actors walk – through surveys, field walks have been 213 used during the research period. For systematizing purposes, the research techniques are divided 214 into four groups: 215 generation. The participation and observation technique were applied frequently to understand 216 the socio-institutional aspects. Attending both formal and informal meetings, socializing through 217 friendship and networking were essential methods. The participation in water distribution and 218 drainage management activities as observer has improved the quality of the research. The other 219 activity which has helped to conduct socio-technical research was the Follow the Innovation 220 (FTI)8 activities of the project. In WUA Koshkopir Ashirmat, FTI activities on Strengthening of 221 WUAs through Social Mobilization and Institutional Development (SMID) were started during 222 the research period. The objective of the innovation is to transform the existing, weak water 223 users association (WUA) into a real functioning WUA through social mobilization and 224 institutional development approach (SMID). The process of FTI has helped to apply a 225 transdiciplinary approach for socio-technical research. A series of stakeholder meetings and 226 workshops were organized within the FTI framework where socio-technical aspects of water 227 management were discussed with a large group of stakeholders. 228 Socio-technical analysis of water management: application of the research framework 8 surveys, studies, participation and observation, and expert knowledge For a detailed report on FTI for WUA component see Abdullaev et al. 2008. 10 229 Water management at grass root levels: socio- technical analysis of water management in WUA 230 Koshkopir Ashirmat 231 The WUA Koshkopir Ashirmat has 2116 ha of irrigated land. It was organized in place of 14 232 brigades of formerly two collective farms (figure 5). The map shows that before the de- 233 collectivization (2005) there were 14 brigades, which were growing mostly cotton and rice. In 234 2005, in place of former 14 brigades more than 70 individual farms have been established by 235 land commission The different colours in figure 4 before the de-collectivization indicate different 236 brigades and after different individual farms. The individual farmers have been assigned to grow 237 cotton, wheat (50% of individual farmers), vegetables and livestock. The irrigation and drainage 238 network, formerly managed by the collective farm has been assigned partly to WUAs (the former 239 on-farm canals and pumps) and individual farmers (the tertiary and below level irrigation 240 canals). 241 242 Figure 5. Pre and post reform maps of Koshkopir Ashirmat Water Users Association 243 (WUA) 244 The irrigated areas receive water from the Zeu Yop canal which is fed by the Polvon main canal- 245 one of the largest irrigation networks in Khorezm region. Human-made water scarcity due to the 246 competition for water resources at the head of the Zeu Yop canal results in abandoning of 247 considerable parts of the irrigated agricultural fields in the tail end of the canal –150 to 200 248 hectares were not cultivated in 2008. These plots are regarded unsuitable for cultivation at the 249 moment by the local hakimyat due to water scarcity. 11 250 The water is delivered to the WUA Koshkopir- Ashirmat through the territory of other three 251 WUAs, located upstream of the study area. This situation creates an unsustainable and non- 252 reliable water supply. Although the irrigated area within the command system of Zeu Yop canal 253 has not been increased since mid 1980's, the water supply to WUAs has become very much 254 contested by both WUAs and individual water users along the canal. Hence the main attribute of 255 water management in the study area is “constructed water scarcity” (Oberkircher and Ismailova. 256 forthcoming). Both water distribution between neighbouring WUAs and within water users of 257 the study WUA is skewed and unequal in physical terms. The way water management is 258 organized ---is a reflection of the internal social dynamics which has been shaped by a few 259 important elements of the everyday water management. These aspects are ownership of irrigation 260 drainage infrastructure, formal and informal institutions, agents, resources and emerging 261 collective action. 262 Contested nature of water infrastructure and its impact on water control strategies 263 The transformation of the water system from collective farms to WUAs has brought changes in 264 water and drainage infrastructure ownership. The major water control strategies applied by 265 different groups are shaped by following aspects of infrastructure ownership. 266 1. The existing inter-farm irrigation and drainage network has stayed under control of state 267 run water management organizations (WMOs). The reduced workforce and declining 268 budgets in mid 1990’s due to the overall economical decline in Uzbekistan have left this 269 level virtually unattended by WMOs staff. As a result water users, mostly large farmers, 270 have installed different types of pumps along the canal system, practicing technical water 271 control, reducing the water shares of the WUAs located in the tail end of the irrigation 272 system. 273 2. The ownership of the collective farm irrigation network has been distributed between 274 WUA and individual farmers. The field and tertiary canals has been assigned to the 275 farmers and secondary canals to the WUA. Numerous pumps of the former collective 276 farms have been also assigned first to WUAs. However, a few years of operation have 277 created problems in payment for electricity, of diesel for pumps and for maintenance. 278 Therefore, almost all WUAs in the study region (Khorezm) have re-assigned pumps to 279 the individual farmers. The property regime created by transformation of pumps to 280 individual farmers has legitimized the wider use of pumps. 12 281 3. The drainage network of the former collective farms has not been specifically assigned to 282 WMOs, WUAs or farmers. This has resulted in a plurality in responsibility for operation 283 and maintenance of the drainage system. The maintenance of the drainage system at the 284 former collective level has been left to the farmers. In quite a few cases they have cleaned 285 “their part” of the drainage system. This gave them the claim to the ownership of water in 286 the drainage ditches. Furthermore, the farmers claim the right to block the drainage 287 system and pump water for their needs whenever the canal water becomes scarce. 288 Institutions9 and their implications for water control 289 De-collectivization has resulted in a different socio- political situation and led to the formation of 290 new and different interest groups in the study area. There are at least three different groups of 291 farms in rural Uzbekistan (Trevisani, 2008). The first group of farms is under state quota, 292 growing cotton and wheat for the state with 10 to 20 ha of irrigated land per farm .The second 293 group produces more commercial crops, such as rice, vegetables and fruits with land sizes 294 around 1 ha and less. The third group are smallholder landowners who grow mainly crops for the 295 subsistence of their livelihoods. However, the state-quota farms may also grow rice and they 296 may have smallholder land in their backyard (Veldwisch, 2008). 297 Our research has identified the institutions with direct influence on water management are 298 shaping the water control strategies of the actors involved in the process. The institutions are 299 both formally and informally embedded in the society (Long. 2001). The formal institutions are 300 part of the current state policies, informal institutions are rules, regulations and relationships 301 .crafted and established by local people. The informal institutions in study area are shaping also 302 behaviour of the formal institutions. 303 State- quota 304 The state quota for cotton and wheat has the following important implications for water 305 management: (i) water is seen as one of the inputs into the cotton- wheat quota production. The 306 water management institutions (organizations, water rights, legal documents) are subordinate to 307 agricultural planning. The water contracts are prepared only for cotton- wheat farmers and 308 WMO, WUA are made responsible during the irrigation season to treat cotton-wheat farmers as 309 priority (ii) the state quota system makes possible administrative interferences into the everyday 9 Institutions are rules which enable and also restricts human agency. Institutions provide a certain reliability of expectations for individuals (North. 1990) 13 310 water management. The state quota gives a space and supports to farmers who cultivate state 311 quota to apply socio- economic and political water control strategies. They can complain to the 312 hakim about the water “scarcity”, they can apply pressure on WMO and WUA managers if water 313 is not delivered to their fields on the agreed schedule, they can request for pumps to be installed 314 into the drainage system, etc. However, at the same time the state quota system gives 315 opportunities for the hakim and state organizations to interfere into WMO and WUA matters. In 316 the study WUA, the Council Chairman was replaced two times, once by the provincial hakim 317 and the second time by the district hakim. The state quota system also allows for local water 318 users to get investments for their irrigation networks. During the 2008 season, WMOs cleaned 319 two main canals of the WUA at least a few times and two pumps were installed in the inter-state 320 (Uzbekistan-Turkmenistan) drainage canal to pump water for irrigating tail end cotton fields. 321 This shows that the state-quota system, while seemingly a top-down, directive system, is actually 322 the institution that links demands of the state with needs of state quota farms. However, the state 323 planned intervention (state quota) is not accepted or implemented by local actors at face value. 324 The implementation of state quota is shaped by the social interests of the different groups. For 325 instance, according to the state quota the irrigated lands of the farmers who grow cotton and 326 wheat are to be irrigated first. However, when water arrives actually first water is given to the 327 smallholder plots where food crops are grown for mostly consumption purposes (wheat, 328 vegetables, and fruit trees). This rule is accepted even by state quota farmers. The interviews 329 with selected quota farmers reflected that they were made aware by local leadership during 330 wedding parties, funeral process (social gatherings) of the fact that most of the local population 331 are for giving water to the smallholder plots first. The pumps installed by state WMO to serve 332 cotton- wheat areas also used to irrigate non- quota farms and smallholder lands. 333 Asvak- Water turns 334 The water turn, or asvak in local language, is an institution which existed even before the 335 Russians came to the region. The asvak means that each water user group (WUA, village, sub 336 canal) and individual water user (farmer, dehkan, household) has a turn in getting water during 337 the irrigation season10 in the irrigation schedule. The asvak is applied only if the amount of water 338 is not enough to supply water simultaneously to everyone. The asvak has several levels. There is 10 In Uzbekistan irrigation season starts from 1st April and continuous until 1st of April. There is so called winter season, from 1st October until end of March when winter wheat is irrigated, salt leaching is conducted 14 339 asvak between main canals , asvak between districts, asvak between WUAs and asvak within a 340 WUA (between secondary , tertiary canals, between farmers located at the same canal and 341 between farmer and dekhans located at the same field channel (arik in the local language). 342 Although asvak is generally regarded as a very effective tool for water allocation during water 343 shortages, it does not work every time and everywhere. According to the water users (owners of 344 individual farmers, surveyed during the research), the asvak institution has become less effective 345 in recent years due to the fact that it is planned by the local hakimyat jointly with the WMO, with 346 no communication with the water users, villages and WUAs. As a result, the asvak is contested 347 constantly by a large group of water users. However, there are some “re-designed”, adapted 348 versions of informal asvak in place in every WUA, village and location. Our research shows that 349 even in the most water shortage periods and locations, local people apply some sort of water 350 turns between different groups. For instance, in spring, the study village received water after a 351 long period and the water was given to the family plots first (yu tomarka). However, in the 352 summer, the cotton was given the highest priority over other uses. It seems that the informal 353 asvak has a very well structured system. The local power structures, such as mahalla leadership, 354 former chairman of collective farm and staff of WUAs are supporting this informal- 355 unstructured/localized asvak. The asvak is a water control strategy for different groups, e.g., 356 hakims organize asvak in order to fulfil their role as government representative in the area; the 357 WMOs because of their role as water management organization of the state, etc. However, asvak 358 is frequently interrupted by the same hakim or WMOs because of their own interests (to deliver 359 water to some of their clients) or due to the reduced water levels in the canal. Furthermore, 360 WUAs, villages and individual water users frequently use technical water control means (e.g. 361 permanent or mobile pumps) to disturb official asvak. 362 Mahalla- neighbourhood- village 363 Mahalla or neighbourhood (sometimes also used as village) is a very old institution of Uzbek 364 society. Although for the last decade the role and function of mahalla has been greatly shaped by 365 the state building process (Trevisani. 2007, Kandiyoti. 2003), it is still very much alive and 366 fulfils functions related to the daily life of the local people. Mahalla is a collection of different 367 clans and individuals with few formal and more of local rules in place to bring a more organized 368 system into the people’s everyday lives. Since ancient times, mahalla has been dealing with 369 marriage and divorce issues, feeding people and families in need, settling conflicts and issues 15 370 between families and individuals. For the last decade, mahalla was also given the role of the 371 distribution of social welfare among the most needy. In the water control context, mahalla 372 applied its role as a branch of the state at the village level. According to the Uzbek government 373 system, heads of mahalla’s and the council of mahalla leaders represent the state in the 374 neighbourhoods. Therefore, leaders of the mahalla practice political water control strategies in 375 order to both promote the interests of their neighbourhoods and their own. t. The mahalla, as a 376 part of the state apparatus at the local level also seen by local people as legitimate institution to 377 complain on water related problems. The leader of the mahalla has been also urged by local 378 hakimyat to take bold role in everyday water management at former collective farm level. Due to 379 the weak position of t WUA position of mahalla leader became stronger on water management. 380 Qarindosh- relatives- clan 381 During the soviet era, the central state in Moscow attempted to modernize Central Asian 382 republics by eliminating the clan system. However, at present there are many elements of clan 383 networks in all five states of the region (Collins. 2004). According to Collins (2004), the clans 384 are an “informal institution”, with unwritten rules, norms and social conventions. The clans are 385 network for social and political exchange between their members (Collins. 2004). The clans are 386 one of those institutions which apply social power for controlling access to the resources for its 387 members (van Dijk. 1993). The clan system in the study area re-emerged due to the fact that 388 members of a few families have been very successful in the state system. This successful uplift 389 into the highest political levels of the country has nurtured a clan system around nuclear families 390 of those successful family members. Now members of the clan are claiming their right for 391 getting access to the different resources and for special treatment because of their status within 392 the state apparatus. Members of the strongest clan in the study area also keep a few important 393 positions within the local set up. The research have revealed that the clans apply socio- political 394 water control, i.e. the leaders of the clans apply pressure on the hakimyat, the WMO, WUA and 395 electricity companies for getting water to their location and fields of their clients/members. 396 Actors and their resources 397 In study WUA Koshkopir Ashirmat, authors have studied role of three main actors on everyday 398 water management. The three selected actors are mainly those of leading actors, who has very 399 strong both official and informal positions within village (table 1). The table 1 is presenting 400 official and informal positions of the three selected actors. 16 401 Table 1. Actors and their positions within the community in WUA Koshkopir Ashirmat # leaders Positions 1 Chairman of rural council + his circle (relatives, classmates, official status as village council former collective farm management) head 2 3 relative of high official farmer, who owns land level state Former manager of collective farm + his allies (relatives, classmates, people whom he worked during the collective farm) Son of long served collective farm chairman ( son of Rais) Head of a crucial network of existing managers and authority Relative of academician Chairman of MTP and his group The manager was chairman (rais) for years a high level 402 403 WUA is not capable fully utilize its role as major water management unit at the village level due 404 to the limited financial and staff capacities. Therefore, other people than the WUA staff are 405 taking the lead in water management. E.g., the above listed leading actors use the WUA as a 406 platform to promote their candidates for the position of WUA Council Chairman, using their 407 positions within official status they also participate in everyday water management. 408 The leading actors commonly apply the following types of resources: (i) regulatory resources- 409 their access to decision making on water allocation, (ii) information resources- access to 410 information regarding water allocation and distribution, (iii) professional resources - links with 411 water management organizations (or individual bureaucrats in the water sector), (iv) 412 administrative resources - access to local government office (hakimyat), and (v) technological 413 resources- access to technologies and infrastructure on water network. The application of the 414 different resources depends on the position (socio-political network) and agenda of the actors 415 (table 2) 17 416 Table 2. Main actors and their resources in WUA Koshkopir Ashirmat Main actors Resources MTP chairman access to crucial information ability to influence state quota resources distribution access to the resources (money) of clan distribution of mechanical hardware to the farmers access to the water distribution decisions , asvak list of both WMOs and internal (WUA) Rural Council chairman access to and distribution of state social security package ( payments for poor families, money for support children) access to the resources (money) of clan influence on land distribution decisions has most important say on internal asvak Former collective farm chairman access to clan resources access to the decisions by Mahalla leaders His personal links with his former friends Kinship relations with most of villages’ “respected people” 417 418 419 Collective action The physical attributes and features of the irrigation system of WUA make collective action the 420 prerequisite for everyday water management. Any group or individual water user alone is not 421 capable of managing the irrigation system which was originally designed and built for water 422 supply to large collective farms. The main irrigation canals of WUA Ashirmat have no single 423 water regulation gate, because during collective farm days water was taken to the irrigated field 424 by 12 large pump units. These pumps require both a workforce and financial inputs for 425 operation. Only if the farmers work together they can afford the pumping costs. After the de- 426 collectivization pumps were transferred to the WUAs. At the end of the irrigation season, the 427 WUA evenly distributed the pump costs among its large farmer members. Smallholders did not 428 pay for the cost of pumping. The large farmers charged their share of costs on pumping against 429 state credits paid for the cotton or wheat quota. However, in most cases the payments were 430 delayed and the WUA was fined for non-payment. In year 2007, the WUA have assigned the 431 operation and maintenance of the 12 pumps to the cotton-wheat farmers who have access to the 432 state credits and subsidized inputs. The assignment of the pumps to the individual farms helped 433 the management of the WUA to reduce their debt to the Electricity Company, and it led to the 434 formation of water users groups around the “privatized” pumps. 18 435 The other reason for collective action is that the water discharges of the big and old pumps are 436 much higher than the irrigation needs of the largest farmers (e.g. 100 ha). The pumps were 437 designed for irrigation of a brigade (>200 ha). Therefore, in one run pumps are able to deliver 438 water to two or three farmers or dozens of smallholders. Therefore, irrigation was organized by 439 groups of smallholders from the same mahalla. During the field work authors have witnessed 440 frequently when the farmers of the same tertiary canal/pump worked often together for irrigating 441 their crops. The other collective action was on maintenance of the irrigation and drainage 442 network. Due to the huge size of canals and drainage network, large machinery and a large 443 workforce is needed. Again this cannot be provided by a single water user. Therefore, in most 444 observed cases during the field research, the resources of farmers and smallholders were joined 445 for maintenance of the irrigation and drainage network. The collective action is promoted by 446 institutions listed above; the active role is taken by mahalla and clans. 447 The water users also act as group (collective action) on appealing to the hakim and other state 448 organizations to request release of water for their area. E.g., in 2008, around 20 farmers and local 449 smallholders from WUA Koshkopir Ashirmat visited at least two times both the provincial and 450 district hakim to appeal for water for their fields. This indicates that water users has capacity to 451 form a group is a resource for organizing the exertion of pressure. 452 The collective action observed during the socio-technical analysis potentially could be an option 453 for strengthening of WUA. Water users at different channels managed by different WUAs 454 presently only form collective action groups for short periods, until they receive water into their 455 areas. Carefully planned social mobilization activities by WUA management may help to turn 456 this temporary collective action into more systematised water users groups (Abdullaev et al. 457 Forthcoming). 458 The findings of the field research suggest that many familiar aspects of contested canal irrigation 459 management as documented in the international literature (Mollinga. 2003) are starting to find 460 their location specific expression in Uzbekistan. 461 462 Lessons Learnt: outcomes of socio- technical research and conclusions The process of the social differentiation of agricultural producers is in its early phases and is still 463 to express itself fully due to strict state control of agriculture and social life in general. However, 464 the different groups started to apply physical and socio-economic water control strategies for 465 getting access to water. People are increasingly using means of social control for getting access 19 466 to water resources. For example, the farmers with larger irrigated land and higher incomes can 467 afford to buy diesel or electric pumps for organizing irrigation of their fields. They usually allow 468 neighbouring farmers and smallholders to use water, but only if they pay for the cost of operation 469 of the pump. The smaller land owners and weaker groups are not represented in WUA structures 470 at present. The standard bylaws of WUAs establish membership on the base of land ownership, 471 i.e. only heads of the registered farm units can become a member. However, most of medium (up 472 to 1 ha) and smallholder (less than 0.5 ha) water users are not registered as farm units. This 473 already creates inequality and the WUA consequently is not representing all water users of the 474 area. Therefore, it is very important to have a mechanism for inclusion of small farming units, 475 water users using water for other purposes (e.g., fishing, construction/brick making), and the 476 households who depend on the irrigation network for their water for daily uses (domestic water 477 use.). In this study WUA, there are three lakes where people catch fish. Many families use the 478 irrigation network for household water use. However, they are not members of WUA. On paper, 479 the water plan (the allocation schedule) provides access to water for these types of water users as 480 well. In practice, however, the daily water distribution is a different process. Water distribution 481 in comparison with allocation is a more decentralized process, because of the huge irrigation 482 network and many actors involved at each level. 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