1 Institutional Changes for IMT1 in Thailand—What’s Wrong? Han Hongyun, Ph.D/ Professor Chinese Academy for Rural Development, Zhejiang University, Hangzhou, Zhejiang, 310029, China Email: hhyzlg@yahoo.com.cn Abstract: From the perspective of institutional structures over irrigation systems, there are three stages of water development in Thailand: traditional farmer managed irrigation systems, irrigation systems under governments’ responsibilities, and participatory management. Thai Government has specified participatory management framework to enhance the mutual understanding among the Government and user farmers. Unfortunately, this top-down participatory management was largely a failure due to a shortage of clarified laws, overlapped irrigation management agencies, and lack of water pricing policies; in addition to the formal institutional arrangements, the broken down of social cohesion, changing social patterns, lack of conflict resolution mechanisms, and shortage of leaders resulting from dependence culture. All these diminish the effectiveness and efficiency of institutional arrangements for water resources in Thailand. The concentration of power in the bureaucracy, the absence of accountability, the lack of an effective judicial mechanism, and existence of too many agencies with overlapping policy mandates are the direct reasons for the failure of IMT in Thailand; the lack of consistence between new rules and indigenous rules is the fundamental causes resulted in inefficiency of water management. Accountability is problematic in irrigation systems with officials’ primary accountability upward to their supervisors and to the political level. 0. Introduction Irrigation is the largest consumer of water in the world. In Thailand, it accounts for 90% of annual withdrawals. Increasing the productivity of water lies at the heart of water management because of the high volume of agricultural water consumption. A number of countries changed their institutional structures over irrigation systems in the nineties due to the failure of state control, shortage of financial capacity, and the aim of poverty alleviation, the most important one among them is participatory management; nevertheless, there is no agreement as to what institutions will accomplish these goals (Acheson, 2000), “countries that have transferred management of resources to local users have experienced mixed outcomes” (Katon et al., 2001, p.2), “it is not obvious what approach or approaches work best for decentralizing management and increasing the role of users in irrigation 2 management” (Easter, 2000, P. 75). Thai Government has specified participatory management framework to ensure the mutual understanding among governments and user farmers. Essentially all of these pilot experiences have failed to produce sustainable, self-reliant water user organizations (WUOs), “farmer organizations and artificial government partnerships with them have all collapsed after the end of the projects” (Suiadee, 2002, p.300). Judging from the low number of Water Users Cooperatives (WUCs), the level of activity of cooperatives in Thailand is quite ambiguous (Molle et al., 2002), the process of IMT have not progressed smoothly due to the lack of comprehensive understanding on institutional preconditions for IMT. Under a belief of academic and policy debate about appropriate resource management directions will benefit from a detailed and localized understanding of the way in which IMT can work best or why IMT cannot function well, this paper is to examine the institutional changes for IMT in Thailand, including the changes in water laws, water administration, and water policies. Using an institutional and ecological mode of analysis, this study aims to increase our understanding of an important area of the intersection between socio-economic and water resource management, and to find out the likely adverse factors resulting in the failure of IMT in Thailand. The remaining of this research report is as follows: in section 1, changes of institutional arrangements over irrigation systems in Thailand are given, a historical review of the development process of irrigation systems in Thailand will benefit the understanding of institutional changes for IMT; in section 2, what was wrong in Thailand is argued, in this part, I hope to find out institutional factors resulting in the failure of IMT in Thailand; finally, short conclusions are drawn. 1. Changing institutional arrangements over irrigation systems 1.1 Traditional farmer management irrigation systems (FMIS) In the early days, more than two thousand FMIS existed in the northern parts of Thailand alone, which played a critical role in ensuring sustainable agricultural development and in providing legitimate imposition of social control and conflict resolution until the beginning of 20th century (Shivakoti, 2000). Based on canal networks, farmers were organized and formed water 3 user committees. Under socially and culturally embodied custom and norms, each household was obliged to contribute labor, construction materials such as bamboo, logs and stones, and tools for the construction of weirs based on their landholding and economic status. Since the weir as well as entire irrigation system was considered as common property, the households had common rights and responsibility for system repair and maintenance. In general, a FMIS committee was divided into two levels for efficient management of water resource, including a system level and a canal level. The former was the main body for O&M of the entire systems, while the later mainly took responsibility for the management of secondary canals. The district head was the chief of system level organization and the sub-district head become deputy chief at village level with the subordinate of village heads. There were some other positions such as water messenger and ditch headman (See Figure 1). Weir Chief was the main position established at system level even after intervention of RID, who possessed highest authority and made final decision in all affairs; the deputy chief assisted in overseeing water usage by member of the system, allocating water through zoneman, helped in maintenance by checking labor and equipment during repair work, and also assisted zoneman in conflict resolution. Water messenger was responsible for delivering messages, such as scheduling of meeting, water delivery, repair and maintenance and amount and type of equipment, from chief or deputy chief to water users and also reporting back to the chief (Shivakoti, 2000). These traditional irrigation systems provided a strong basis through heavy demands on labor and a complex social organization for wet season rice cultivation, the entire weir community was an autonomous unit technologically and organizationally. Consequently, the communities had easy access to and control over means of water allocation as well as enforcement of norms such as regulation and dispute settlement; the autonomy was often expressed symbolically in the weir spirit cult. The cohesion and social bounds among members are the main reasons for the success and sustainability of traditional schemes which have been under existence for hundreds of years. 1.2 Government’s control over irrigation systems Historically FMISs have experienced two significant periods of change over the last century. “The first, between 1888 to 1933, concerned a periods of 4 extensive administrative and governmental reform. The second, beginning around the mid 1950’s, involves the modernization of agriculture and the shift from subsistence farming to production for market”(TanKimYong, 1995, p.22). As the largest foreign exchange earner, the increased demand for rice export played a critical role in the process of government’s takeover of FMISs. The growth of urbanization and international trade have led to the emergence of large-scale irrigation projects sponsored by government because policy-makers realized in the 1960s that ‘agricultural-export-led-growth’ would require the development of and the control over water resources. With her political power through existing irrigation codes and limited financial resources, Thai Government intervened in communal irrigation technology by establishing water-intake regulators at traditional FMISs, and also established a number of new irrigation systems managed by salaried personnel. Direct government involvement in irrigation began in 1902 when a canal department was formed to develop lowland waterways, control floods, and build and operate minor irrigation works. In 1927 the canal department was reorganized as the RID (Projects department, 1986). Given the situation of political and economic transformation, almost all FMISs were taken control by Government under the clause of technical improvement, the RID was responsible for construction, water allocation, O&M of irrigation systems (See Figure 2). As a result, farmers lost their autonomy and were forced to greater technological dependence on Government. The increasing demand of turnover of irrigation systems from farmers to governments is not founded in an altruistic motive of policies; in many parts of Asia, governments tried to construct large-scale irrigation systems to extend irrigated areas to meet the demand for rice export and cash crops (Barker et al., 1984, p.26). 1.3 Participatory Intervention of Government Since the 1970s, largely driven by government fiscal shortages and strong push of donors, governments around the world have adopted programs to devolve responsibility for irrigation management to water user associations (WUAs), couched in the idiom of community empowerment, participatory management, accountability, capacity building, cost sharing, economic efficiency, and privatization(ADB, 2001). The first attempt of participatory intervention of government started in the year 1962, a first attempt to design 5 WUOs was recorded in 1963 in the northeast and led to the foundation of the first legal WUA in 1966 (Poolswat, 1992). In 1967, RID introduced the concept of WUA in Northeast Thailand and in 1968 in Central Thailand. For the effective implementation of irrigation project and encouraging people’ participation, the Government initiated land consolidation program in the year 1969, the aim was to delegate irrigation and drainage control to farmers. The current constitution also stated that the state must promote and support people participation in natural resource management and determining policies and decision-making in all levels. In addition, the Sub-district Councils and Sub-district Administrative Organizations (SAOs) Act (1994) stated that SAOs must be allocated power to develop plans and implementation to conserve their natural resources (Kijtewachakul, 2003). Moreover, the government tried to reduce the time and work load of farmers by appointing irrigation technicians and staff for better water allocation and distribution at the farm level. After the well recognition of people’s participation and governance on O&M of irrigation systems by the government, the farmer-managed systems in the country have been facilitated and supported by the Government. Although management responsibilities have been shared by government and farmers, government owns the large and medium scale irrigation systems, farmers are only responsible to manage on-farm irrigation canals. RID manages, operates and controls almost all the irrigation systems up to tertiary level on behalf of the Government, farmers under current participatory management are allowed to maintain and operate their systems only at the field channel level .“Donors strongly pushed for the establishment of water user organizations. This top-down initiative was largely a failure, in particular in Thailand”(Molle et al., 2002, p.13). 2. Institutional factors leading to the failure of IMT Over the course of the past thirty years a consensus has begun to emerge that management of resource is basically an institutional problem, according to Johansson, “the term ‘water institution’ broadly refers to the legal institutions of water distribution, to water management and allocation institutions or water administration, and water policies”(2001, p.21). Here I want to follow North’s institutional mode and focus on formal and informal institutional arrangements 6 for water allocation and management in Thailand, and try to find out the likely institutional factors resulting in the failure of IMT. 2.1 Formal institutional arrangement in Thailand 2.1.1 Inconsistence in laws concerned with water resources According to section 1355 of the Civil and Commercial Code (1923), “a riparian landowner has no right to withdraw water in the amount exceeding his reasonable need to the prejudice of other land abutting the same waterway”. The private irrigation act (1939) allows the Government to control all kinds of private irrigation except those which are temporary or serve an area less than 200 rai. The Public Irrigation Act (1942) empowers the Government to control the use of water for agriculture only in the “irrigated areas”, where farmers must obtain permission from government and pay a fee when water is drawn from irrigation canal. The land consolidation act (1974) is applied only to land under the land consolidation area. Property rights that assure users the ability to derive benefits from resources over the long term are necessary to induce them to bear the management cost, “devolution programs that transfer responsibilities for resource management to local users often fail to transfer commensurate rights”(Katon et al., 2001). When irrigators are asked to take over maintenance work, but do not have rights to the water in the systems, user farmers have no incentives taking responsibility for irrigation system management. Thailand is a country with a large number of laws relating to water resources, but it does not have a comprehensive water law which establishes a comprehensive framework for water utilization and management. A serious attempt to reform the water law started around 1991 when a variety of water problems appeared. The first draft national water resource bill faced strong resistance from the authorities because it will loosen state control over water resources and state officials still believe that local people could not manage natural resources. 2.1.2 Overlapped irrigation management agencies One of the big issues with water management in Thailand is the lack of clear guidelines on water resource development supported by the Government. There are 28 agencies in five ministries working for water resource development and two national committees attached to the prime minister’s 7 office—the national water resources committee and the national rural development committee—are, in theory, responsible for drafting water guidelines and coordinating activities of these agencies (See Figure 1). One of the most difficult tasks to implement IMT is that not all stakeholders gain from the proposed changes. The big losers are likely to be the over-staffed irrigation departments and water supply agencies (Easter, 2000). There is no single administrative body that takes responsibility for water quality planning and management of the basin as a whole. Up to now, integrated water resource management has not yet been put into practice in Thailand. Fragmented departments are responsible for water allocation and management, each has her own aim to implement water policies. no legally-recognized apex body is able to guide the operation of such departments to the same direction, an integrated regional development is clearly inhibited by the departmentalized mode of planning on sectoral issues without proper co-ordination mechanisms. 2.1.3 Lack of water pricing policies Water pricing has so far not been tackled in a truly market determined framework even in developed economies such as the USA, where irrigated water is still supplied at nominal rates unrelated to costs of supply, the reasons for this are that in most countries water services are publicly owned and their prices are administratively determined. In Thailand, there exists some legal basis for adequate water pricing in principle, two most important acts for cost recovery are the Irrigation Act of 1942 and the Land Consolation Act of 1974. The State Act of 1942 allow the RID to impose a charge of up to baht 5 per rai for irrigators and for all other users. With the passage of time, the five baht maximum fee became badly outdated and in fact uneconomic to collect (Project Department, 1986). The revenues siphoned off from rice cultivation by the State through the mechanism of the rice premium not only provide the causes for subsidizing water utilization, and in turn result in the difficulty for water charge corresponding to an increase in production costs which cannot easily be passed to the consumer. No fee is charged for irrigated water in Thailand (Molle, 2002), the costs associated with producing irrigated water are positive and inevitably borne by the government (Kumar and Young, 1996). At the same time, water management deficiency has compelled farmers to 8 make considerable investments in pumping devices in order to access water. Thai farmers have been very responsiveness to water scarcity, in particular by developing conjunctive use and pumping capacities (Molle, 2001) and have increased their reliance on groundwater to deal with dry season shortages due to the conflicting government policies, farmers have been subsidized to sink shallow wells as an alternative water source (Flatters and Horbulyk, 1995). 2.2 Informal institutional arrangements in Thailand 2.2.1 The broken down of social cohesion There is little question that appropriately designed modern irrigation works can enhance the efficiency of many farmer-organized systems, the large and medium scale irrigation systems are playing an important role in the development of irrigated agriculture in Thailand (See Table 1 and 2). The construction of large and medium scale irrigation systems has frequently been funded by external sources, and these external sources substantially reduce the need for mobilizing labor to maintain the system. But interventions designed by outsiders that ignore the potential disruption of the mutual dependencies and reciprocal relationships among farmers may cause more harm than good (Ostrom and Gerdner, 1993). Maintenance is essential to preserve access to water for those whose plot is not located along canals. In most areas, farmers are now widely contributing to cleaning and grass-cutting by gathering money, huge excavators are widespread nowadays and can be easily rented for a reasonable price. It has also been observed that the burden of maintenance, as well as on-farm development, has partly been transferred to local budgets. With the decentralization and the possibility for farmers to have a say in the allocation of some funds, more and more operations of ditch digging or dredging are passed on to the sub-district or to district budgets. The cooperative maintenance of the ditches was the main reason for the farmers of a WUG. Physical capital including any engineered works, such as dikes and irrigation canals, provides a basis for communication and dependence among farmers. When labor is the primary medium of exchange, investment in public infrastructure is easy to monitor. “Shared norms that reduce the cost of monitoring and sanctions activities can be viewed as social capital to be utilized in solving CPR problems”(Ostrom, 1990, p.36). 9 2.2.2 The heterogeneity of social patterns Social scientists are paying increased attention to the implications of heterogeneity, heterogeneity of individuals sharing a resource and heterogeneity of the resource itself, in the management of commons (Mcpeak, 2003). An important factor contributing to the success of WUGs comes with situations in which farmers heavily depend on irrigated agriculture for their livelihoods. Farmers with much land or large families may be more interested by water issues, while those with poor water conditions have turned their attention to other activities (Katon et. al., 2001; Molle et al., 2002). Some farmers using an irrigation system begin to obtain significant off-farm income and the resource was thus reduced to marginal economic importance in Thailand. Part-time farmers have little time to devote to collective action and, especially if they are in a favorable location within the hydraulic network, they may be little interested in costly personal investments in terms of commitment aimed at raising the productivity of an activity which is only marginal for them. Meanwhile, more and more new land users substantiated property right issue to land and water resources. The new users were often either new industrial or commercial firms, or absentee landowners. The entry of these new users often meant that traditional methods of settling disputes and of cooperative resource management broke down and also increased the total demand for water in a given system (Flatters and Horbulyk, 1995). 2.2.3 The lack of conflict resolution mechanisms Thailand is a rice-leading country in which irrigation water is an important input factor in rice production. Industrialization, urbanization, and increasing concerns over environment have increased the demand for limited water and contributed to dry-season water shortages and created conflict over water, including conflicts between water users among different sectors, within one hydrologic region, and even in one water user groups. Rules are generally devised with compliance costs in mind, which means that methods must be devised to ascertain that a rule has been violated, to measure the extent of the violation, and to apprehend the violator (North, 1990). Most commonly village headmen and sub-district heads, more rarely other local leaders, are called in to solve a dispute; a compromise is found in order to avoid social disruptions 10 because mutual monitoring and enforcement “involve relatively high personal costs and produce public goods available to everyone” (Ostrom, 1990, p.94). The lack of conflict resolution mechanism contributed partly to the low efficiency of water management. 2.2.4 The lack of leaders resulting from dependence culture As a social process of resource management performed in a given historical context and constraining physical environment, “the patterns and effectiveness in managing water appears to be closely related to the characteristics of the society concerned, its history, social structure and culture”(Molle, 2001, p.13). Within strategies to promote decentralization, improvement of the capacity of the human resources for decentralized planning is paramount, the lack of local leadership is also a contributing factor to the failure of the WUOs. Values in Thai society play a critical role in it. Farmers try to obtain a change in their favor by approaching people with adequate power and who are expected to behave as patrons. These patron-client relationships are common in Thai society. Individualism and avoidance also inhibit community participation in collective actions (Rubin and Rubin, 1973). So local individuals are not willing to act as the leaders of WUGs, or they are not ready to act as leaders due to the lack of confidence as a leader due to following features: “first, most local elected officials serve their cities part-time; second, local elected officials resent being trained; third, local elected officials quickly become overwhelmed by the technical complexity of the public issues; fourth, local elected officials tend to ‘over manage’ and ‘under lead’; fifth, local elected officials choose not to develop their governance capacity concerns the supply side of local elected development (Coombs and Miller, 1999). To manage possible conflict, it is quite important for local leaders to be taught the political leadership skills necessary for effective governance that facilitate consensus decisions, techniques for coalition building, a philosophy that expresses the relationship between local water users and representatives of local government. Usually, the Government is not often ready to provide training policies to serve elected and appointed leaders. “Rather than create an opportunity for teaching villagers self-help the higher officials, consistent with their roles as benevolent patron, dominate all action and, in turn, seeks 11 compliance from the villagers”(Rubin and Rubin, 1973, p.271-272). 3. Conclusions Thai Government has specified participatory management framework to ensure the mutual understanding among governments and user farmers. However, the bureaucrats lacking a comprehensive understanding of irrigation systems, including formal and informal institutional arrangements over water utilization and management, have contributed to the failure of IMT. Thai water management institutions are suffering following shortcoming: a shortage of clarified laws, overlapped irrigation management agencies, and water pricing policies. In addition to the formal institutional arrangements, the broken down of social cohesion, changing social patterns, the lack of conflict resolution mechanisms, and shortage of leaders resulting from dependence culture. All these diminish the effectiveness and efficiency of institutional arrangements in resolving increasing competition for water resources in Thailand. So far the Government retains overall ownership and financial responsibility for the system and control over the water resources, water users groups(WUGs) are responsible for maintaining and operating their systems only at the tertiary level. The fundamental issue with IMT is that while public agencies have agreed to share the responsibilities with farmer organizations, there is no significant change in the power relations between officials and user farmers and no mutual accountability so far. Officials have no incentives to foster independent WUAs, WUAs remain dependent on the public organization legally, financially, and psychologically. At present, making irrigation systems completely autonomous is risky due to the physical situation of irrigation systems and the lack of local expertise, reforms need to be carried out step-by-step; however, governments should persevere with reforms to improve the accountability, while exercising overall control through strong regulatory and consultative mechanisms. Accountability is especially problematic in irrigation system management, with officials’ primary accountability upward to their supervisors and to the political level. The key to my argument is that institutional arrangements for IMT should vary depending on the patterns of internal factors of a given group and external factors outside the domain of those affected. The fundamental issue with IMT 12 is that while public agencies have agreed to share the responsibilities with farmer organizations, there is no significant change in the power relations between officials and user farmers and no mutual accountability so far. At present, making irrigation systems completely autonomous is risky due to the characteristics of public goods and physical situation and the lack of local expertise, reforms need to be carried out step-by-step; however, governments should persevere with reforms to improve incentives and accountability, while exercising overall control through strong regulatory and consultative mechanisms. IMT is the abbreviation of “irrigation management transfer”. References 1. ADB (Asian Development Bank), 2001. Water for All: the Water Policy of Asian Development Bank, Manila. 2. Acheson, J., 2000. Varieties of Institutional Failure, Keynote address for the meeting of the international Association for the study of Common Property Resources, June 3, 2000, Bloomington, Indianan. 3. Barker, R., Cowrd, E.W., Levine, G., and Small, L.E., 1984. Irrigation Development in Asia: Past Trends and Future Directions, Ithaca: Cornell University Press, 1984. 4. Coombs, V.V., Miller, M., 1999. Developing the Governance Capacity of Local Elected Officials, Public administration Review, vol. 9, No. 3, p.199-217. 5. Christensen, S.R., 1994. “Water Allocation Conflicts in Thailand: an Analysis of Government Failure,” Water conflicts, second Edition, by Natural Resources and Environment Program, Thailand Development Research Institute and Queen’s University, Canada. October, 1994, p.53-86. 6. Easter, W., 2000. Asia’s Irrigation Management in Transition: A Paradigm Shifts Faces High Transaction Costs, Review of Agricultural Economics, Vol. 22, No. 2, p. 370-380. 7. Flatters, F., Horbulyk, T.M., 1995. Economic Perspectives on Water Conflicts in Thailand, Published in TDRI Quarterly Review, Vol.10 No. 3 September 1995, p. 3-10. 8. Höynck , S., and Rieser, A., 2003. The Dynamics of Water User Associations in a Large-scale Irrigation System in Thailand, Technology Resource Management & Development-Scientific Contributions for sustainable Development, Vol.2, p.1-22. 9. Johansson, R.C., 2001. Pricing Irrigation Water: A Literature Survey. The world Bank Washington, D.C. 10. Katon, B., Knox, A., and Meinzen-Dick, R., 2001. Collective action, Property rights, and Devolution of Natural Resource Management, www.capri,ciar.org, policy brief number 2-January. 11. Kijtewachakul, N., 2003. Institutional Development in Community-based Natural Resource Management: Local Politics and Governance in a Semi-urban Area of Northern Thailand, Presented at "Politics of the 13 12. 13. 14. 15. 16. 17. 18. 19. 20. 21. 22. 23. 24. 25. 26. 27. Commons: Articulating Development and Strengthening Local Practices", Chiang Mai, Thailand, July 11-14, 2003. Kumar, R., Young, C., 1996: Economic Policies for Sustainable Water Use in Thailand, CREED Working Paper Series No 4, International Institute for Environment and Development, London Institute for Environmental Studies, Amsterdam Collaborative Research in the Economics of Environment and Development (CREED). Mcpeak, 2003. Analyzing and Addressing Localized Degradation in the Commons. Land Economics, Vol. 78, No. 4, P. 515-536 . Molle, F., 2001. Water Pricing in Thailand: Theory and Practice, ISBN 947-553-898-1, Feb. 2001 DORAS - DELTA : research report no 7. Molle, F., 2002. To price or not to price? Thailand and the Stigma of ‘Free Water’, Paper Presented at the Conference on Irrigation Water Policies: Micro and Macro Considerations 15-17 June 2002, Agadir, Morocco. Molle, F., Ngernprasertsri, N., and Sudsawasd, S., 2002. Are Water User Organizations Crucial for Water Management? A Post-mortem Analysis of Water User Groups in Thailand and the Prospect for Reincarnation, Paper prepared for the 6th Conference on Participatory Irrigation Management, Beijing, 20-26 April 2002. North, Douglass, C. Institutions, Institutional Change and Economic Performance, Cambridge University press, First Published 1990. Ostrom, Elinor. Governing the Commons-the Evolution of Institutions for Collective Action, Cambridge University Press, First Published 1990. Ostrom, E., Gerdner, R., 1993. Coping with Asymmetries in the Commons: Self-governing Irrigation System Can Work, the Journal of Economic Perspectives, Vol.7, No.4, p.93-112. Poolswat, D., 1992. A guideline for WUO’s Development: On-farm Water Management Branch, Royal Irrigation Department, 15p. Projects Department, East Asia and Pacific Region Office, 1986. Thailand Irrigation Subsector Review, Document of the World Bank. Royal Irrigation Department, People Irrigation Act, The People Irrigation Act was published in the Government Gazette Vol. 56, Part 53, dated 20 October B.E. 2482(1939). Royal Irrigation Department, State Irrigation Act, The State Irrigation Act B.E. 2485 was published in the Government Gazette Vol. 59, Part 62, dated 22nd September B.E. 2485 (1942). Rubin, H.J. and Rubin, I.S., 1973. Effects of Institutional Change Upon a Dependence Culture: The Commune Council 275 in Rural Thailand, Asian Survey, Vol. 13, No.3, p.270-287. Shivakoti, G.P., 2000. Participatory Interventions in Farmer Managed Irrigation Systems In Northern Thailand: Dynamism in Resource Mobilization. The Eighth conference of the international association for the study of common property, Bloomington, Indiana, USA, May 31-June 4. Suiadee, W., 2002. Organizational Change for Participatory Irrigation Management, Report of the APO seminar on organizational change for participatory irrigation management, Philippines. TanKimYong, U., 1995. Muang-fai Communities Are for People: Institutional Strength and Potentials, Chulalongkorn University, Social 14 Research Institute, ISBN 974-632-497-7. 15 People’s Irrigation System Project Level State Irrigation System Irrigation Engineering Project Engineer Water Master Zone Man Farm Level Committees of Water Users Association Chairman and Central Committee Irrigation Committees at Village Level Common Irrigator Deputy Water Messenger Government Official at Provincial/District Level District Officer Deputy Agriculturalists Village Government Officials Subdistrict Officers Village Headman Deputy Chief and Vice Chief of People’s Irrigation Project Irrigation Committee at Village Level Ditch Headman Deputy Water Messenger Government Officials at District and Subdistrict Level District Officer Deputy Agriculturalists Subdistrict Official Village Government Officials Village Headman Deputy Water Users Water Users Figure 1 The Organization Chart of State and People’ Irrigation Systems Source: adapted from “water resources laws in Thailand, department of energy development and promotion, Japan International cooperation agency, the Japanese institute of irrigation & drainage, 1999, p.44. Figure2 Organization Chart of Royal Irrigation Department in Thailand Source: adapted from Suiadee, W., 2002. “Organizational Change for Participatory Irrigation Management”, Report of the APO Seminar on Organizational Change for Participatory Irrigation Management, Philippines, P.297. 16 Chairman Secretarial Deputy Chairman for Water Operation and Maintenance Secretary Deputy Chairman for Other Activities Chief of Section/ Chief of Canal Registrar Treasurer Liaison Officer Chief of Ditch Member Figure 3 Typical Organization Chart of WUG Table 1 Characteristics of Water Resources Development Projects Size of project Large-scale Medium-scale Small-scale Investment cost (million Baht) > 200 < 200 >4 Storage capacity (MCM) > 100 < 100 - Water surface area(km2) > 15 < 15 - Irrigation area (ha) > 12,800 < 12,800 - No. of project 90 825 8,550 Source: adapted from Suiadee, W., 2002. “Organizational Change for Participatory Irrigation Management”, Report of the APO Seminar on Organizational Change for Participatory Irrigation Management, Philippines, P.295. Table 2 Land Utilization in Agriculture, 1999-2003: Unit: 1,000 rai Items 1999 2000 2001 2002 2003 Total land area 320,697 320,697 320,697 320,697 320,697 Agriculture 131,341 131,196 131,060 Farm holding land 131,341 131,196 131,060 Size of farm (rai) 24 23 23 Irrigation 3 30,789 31,238 30,777 31,231 31,454 Area irrigated by large and medium 22,382 22,665 22,008 22,181 22,180 scale-irrigation systems Area irrigated by small 8,407 8,573 8,769 9,050 9,274 scale-irrigation systems Source : 1/ Royal Forest Department, 2/Department of Fisheries, 3/ Royal Irrigation Department. http://www.oae.go.th/statistic/yearbook/2003/indexe.html.