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|Regional report:||Water Report 37, 2012|
Thailand covers an area of 513 120 km2 and is located in the southeastern region of the continent of Asia (Table 1). Its immediate neighbours are Myanmar to the north and the northwest, Lao People’s Democratic Republic to the northeast, Cambodia to the east and Malaysia to the south. The water bodies that skirt Thailand are the Mekong river in the east that forms Thailand’s natural boundary with Laos, the Gulf of Thailand to the southeast and the Indian Ocean and the Andaman Sea to the southwest.
Administratively, the country is divided into 76 changwats (provinces), 4 regions and the Bangkok Metropolitan area. The four regions correspond approximately to the physiographical regions of Thailand: the northern region is mountainous with forests; the northeast is dry and consists of a plateau that borders the Mekong river; the central region is an extensive plain subject to flooding; and the southern part is a peninsula.
About 26.79 million ha are considered as cultivable, which represents 52 percent of the country. In 2009, the cultivated area was an estimated 18.995 million ha. Of this total, 15.300 million were under annual crops (mainly paddy rice) and the remaining 3.695 million ha were under permanent crops.
The climate is mainly governed by the alternation between the southwest monsoon, which brings heavy rainfalls (May-October), and the northeast monsoon, which is comparatively dry and cool (October-February). The transitional period (March-April) is characterized by heavy thunderstorms.
The average annual rainfall is about1 622 mm. It ranges from 1 100 mm in the central plain and the northeast of the country to 4 000 mm in the southern peninsula near the Andaman Sea.
The total population was an around 68.7 million in 2009, of which 66 percent lived in rural areas, compared with 69 percent in 1999. During the period 1999-2009 the annual population growth rate was an estimated 0.97 percent. The population density is about 134 inhabitants/km2.
In 2008, 98 percent of the population had access to improved water sources (99 and 98 percent in urban and rural areas respectively). Sanitation coverage accounted for 96 percent (95 and 96 percent in urban and rural areas respectively).
In 2009, the total economically active population was 39.5 million, or slightly more than 58 percent of the total population. The economically active population in agriculture was around 19.4 million (49 percent of total active population) of which women represented 45 percent. In 2009, Thailand’s gross domestic product (GDP) was US$263 772 million of which agriculture sector accounted for 12 percent.
According to the Food and Agriculture Organization of the United Nations (FAO), Thailand’s yearly hungry people reduce from 16.8 million (30 percent of total population) during 1990-92, to 13.8 million (23 percent) during 1995-1997, and 13.4 million (21 percent) during 2001-2003.
In 2003, food exports accounted for 24.6 million and food imports accounted for 8.4 million tonnes.
Thailand can be divided into seven river basins, but in the literature it is generally divided into 25 subbasins. Figure 1 and Table 2 show the location and the characteristics of the 25 major river subbasins and indicate the total surface water resources, 213.35 km3/year. Aquifer recharge from rainfall is around41.90 km3/year (about 5-6 percent of the total precipitation). Approximately 30.70 km3/year are estimated to return to the river system (overlap). The total internal water resources of Thailand are therefore about 224.55 km3/year.
Thailand shares three major river systems with its neighbours: the Mekong river forms the border with Lao People’s Democratic Republic in the north and east (about 18 percent of the total Mekong catchment area is located in Thailand), the Salween river is on the northwestern border with Myanmar, and the Kolok river is on the southern border with Malaysia. This last river, originating in Thailand and then bordering between Thailand and Malaysia, is very short with a total length of just over 100 km.
The Mekong river constitutes an additional external resource for Thailand, which has been estimated as half the discharge of the river, Thailand’s contribution to this river has to be deducted over a long distance. The flow of the Mekong river at the point where it enters Lao People’s Democratic Republic near Pakxé is about 280 km3/year. The contribution of Thailand to the Mekong river is an estimated 51.9 km3/year This gives an accounted flow of the Mekong border river for Thailand of 114.05 km3/year. The Salween river on the border with Myanmar, with an estimated flow of 200 km3/year, flows only over a relatively short distance on the border. It is therefore considered that there is not much contribution from Thailand over that short distance and the accounted flow is 200/2=100 km3/year.
By adding the internal and external resources together, the total renewable water resources are approximately 438.6 km3/year (Table 3).
Total exploitable water is an estimated 125.98 km3/year, consisting of 75.64 km3/year regular renewable surface water, 27.34 km3/year irregular renewable surface water and 23.00 km3/year regular renewable groundwater.
Total large dam capacity is an estimated 68.28 km3 in 2007, which is about 32 percent of the annual runoff. However, many dams have been over-designed, compared with the annual recharge obtainable. There are four categories of dams in Thailand:
There are five dams with a capacity of more than 5 km3: Srinagarind (17.75 km3), Bhumipol (13.46 km3), Sirikit (9.51 km3), Vaijiralongkorn (8.86 km3) and Rat Cha Prapa (5.64 km3).
There are 5 main dams on the Mekong river basin in Thailand, the Sirindhorn (1 966 million m3), Chulabhorn (188 million m3), Ubol Ratana (2 264 million m3), Pak Mun (114 million m3) and Lam Ta Khong (310 million m3).
In general, Thailand’s international water issues stem from the country’s thirst for water, hydroelectricity, and utilization of coastal areas. The main issues include:
In 2007, total water withdrawal was an estimated 57.3 km3, of which 90.4 percent was for agricultural, 4.8 percent for municipal and 4.8 percent for industry (Table 4 and Figure 2). In 1990, total water withdrawal was an estimated 33.1 km3, of which 91 percent was for agricultural purposes, 5 percent for municipal use and 4 percent for industrial use. Of the total withdrawal of 57.3 km3, 82.9 percent was surface water and 17.1 percent was groundwater (Figure 3).
Wastewater treatment is not common. Industrial wastewater is generally discharged into rivers and canals. About 2 191 million m3 of wastewater were produced in 2003. In 2007, some 523 million m3 of wastewater were treated. Numerous wastewater treatment projects are being developed in the Bangkok metropolitan area. There is no reuse of treated wastewater in Thailand.
Irrigation from river diversion and reservoirs started in the north seven centuries ago. In modern times, canal construction for irrigation started at the beginning of the last century, in parallel with the creation of the RID. The aim was to maintain water in canals for irrigation and navigation, and to drain paddy fields during periods of flooding. Irrigation has traditionally been supplementary irrigation for the wet season. It is only recently that schemes have been designed for dry season irrigation.
The irrigation potential for the wet season can be roughly estimated as 12.2 million ha, considering both soil and water availability but excluding basin transfers (World Bank, 1985). New estimates consider that irrigation potential accounts for 9.5 million ha (Thai Hydrologist Assembly, 2007).
In 2007, the area equipped for wet season irrigation was an estimated 6 414 800 ha. In 2005, the regional distribution of irrigated area in the wet season was 54 percent in the central plain, 18 percent in the north, 14 percent in the northeast and 14 percent in the south. In 1995, the area equipped for wet season irrigation was an estimated 5 003 724 ha, of which 47 percent in the central plain, 24 percent in the north, 19 percent in the northeast and 10 percent in the south.
In 2007, the area actually irrigated was an estimated 5 089 914 ha, or 79 percent of the equipped area (Table 5).
Surface irrigation is the only technology used in the schemes. Sprinkler and localized irrigation are at an experimental stage only for fruit trees. Generally surface water is used, accounting for 90.9 percent of the total area equipped for irrigation (Figure 4).
Early systems were designed to operate at full capacity only in the wet season. The canal capacities and control regulators are inadequate for the increasing demand for dry season irrigation. Furthermore, irrigation water demand has to compete with demand from other sectors. This becomes a sensitive issue during the dry season. A certain flow of water must be maintained for navigation, to prevent saltwater intrusion, and to supply water for domestic and industrial purposes in the Bangkok area. In the dry season, water resources can no longer meet the increasing water demand from all sectors, and particularly from the irrigation subsector, which needs to withdraw more and more water because of the development of dry season irrigation. This water competition has led to poor agricultural performance in recent dry seasons.
Dry season irrigation is practiced on 60 percent of the equipped area, up from 18 percent in 1994.
Small-scale projects are those that can be completed within one year and without land compensation. The schemes that cannot be completed within one year, or that need land compensation are considered medium-scale. Schemes are classed as large-scale if there is a storage capacity of more than 100 million m3 or if they can irrigate at least 80 000 rais (12 800 ha). Irrigated areas can be divided into the three categories(Figure 5):
By 1999, there were 1 985 pumping projects. Essentially these are small-scale projects with electrical pumping from nearby waterways. In 2007, their combined command area was 460 000 ha, mainly in the northeast and north. Water management in these projects is the responsibility of RID and water user groups. Management responsibility is to be transferred to Local Governments.
In 2007, total harvested irrigated cropped area was an estimated 7 387 072 ha. Rice accounts for 6 268 080 ha (2 327 158 ha first season rice and 3 940 922 ha second season rice), or 84.9 percent of the harvested irrigated copped area, vegetables represent 83 421 ha (1.1 percent), sugarcane 256 016 ha (3.5 percent), other annual crops (tobacco, cotton, etc.) 37 396 ha (0.5 percent) and permanent crops 742 159 ha (10.1 percent) (Table 4 and Figure 6). There are also 233 033 ha of fish ponds, which are irrigated and not taken into account in the total, because they are not a crop.
Irrigation development costs US$3 647/ha as follows: construction of head work US$2 187/ha, conveyance system US$860/ha, field system US$600/ha and maintenance cost US$33/ha per year.
Poverty is observed to be concentrated in non-irrigated areas (or rainfed areas).
In total there are 31 ministerial departments under ten ministries, one independent agency and six national committees that are involved in water resources development. They are responsible for water policy, irrigation, domestic and/or industrial water supply, fisheries, flood alleviation, hydropower generation, navigation or water quality.
The National Water Resources Committee (NWRC), under the Office of the Prime Minister, is responsible for setting a policy to develop water resources throughout the country.In general, the Ministry of Natural Resources and Environment (MONRE) is responsible for policy planning while the Ministry of Agriculture and Cooperatives (MOAC) is responsible for implementation.
The National Economic and Social Development Board is responsible for economic planning.
The Department of Groundwater Resources, under the MONRE, monitors groundwater resources, while surface water monitoring is mainly carried out by the Department of Water Resources, and the Royal Irrigation Department, which has its own network.
Many departments or agencies are involved in water supply for domestic or industrial purposes. The main one is the Metropolitan (or Provincial, outside Bangkok) Waterworks Authority. Wastewater treatment and water quality are mainly the responsibility of the Ministry of National Resource and Environment.
Large dams are operated either by RID or by the Electricity Generating Authority of Thailand (EGAT), while small dams have been developed by the Land Development Department or the Department of Water Resources.
The Harbour Department is in charge of protecting inland waterways, and of issuing licenses for navigation.
Irrigation is managed by the RID for public schemes, or by the Department of Water Resources. The RID is the supervising agency for private irrigation.
There are four levels of water user organization in the irrigation areas:
Participatory irrigation management (PIM) and cost sharing in water management are encouraged in all the RID irrigation areas but not widespread.
By 2025, Thailand is projected to have sufficient water of good quality for all users as a result of its efficient management, organization and a legal system that ensures the equitable and sustainable use of its water resources with due consideration to the quality of life and participation of all stakeholders.
Thailand’s nine-point National Water Policy and Vision, as set forth by RID, details how this will be implemented:
Most laws related to water management are outdated. All existing laws are focused on individual aspect of water management and none on a holistic view (IWRM). There is no law specifying water rights. Currently there is a draft Water Law that specifies water rights, river basin organizations and national apex body for water management. This draft passed the cabinet in June 2007, and is waiting for approval from the parliament. Earlier versions of this law have been at this stage before but failed to pass.
In 2004, surface water quality classified as ‘good’, ‘fair’ and ‘poor’ accounted for 48 percent, 32 percent and 20 percent respectively. The classification carried out by analysing the quality of samples of water taken from natural waterways throughout the country. The overall situation has improved compared to 2003. Critical areas are: lower Chao Phraya in central Thailand and Lower Lam Takong in northeast Thailand. In the North, Northeast and South water quality is good (surface water quality) and improving, while the Central is good with mixed improvement, and the East is fair and stable.
In 1999, in the northeast, 10 percent of the irrigated land was affected by salt. The presence of the salt bearing nature of the soil parent material has been identified as the primary cause. Other activities, such as irrigation, could be classed as secondary causes for accelerating this condition locally. Many programmes have been launched to correctly manage cash crops and paddy on saline soils. Salinization is now reported to be affecting large areas in the coastal parts of the central plain.
Bangkok faces problems of both too much and too little water. Flooding occurs frequently in the wet season owing to low average elevation, high tides and inadequate drainage. The Metropolitan Waterworks Authority is unable to supply water to meet all domestic and industrial demand. As a result, in the outskirts of Bangkok, private and industrial abstraction of groundwater exceeds the safe yield of the aquifer. This accelerates the rate of land subsidence (5-10 cm/year), which in turn aggravates the problem of flooding. Indeed, subsidence has caused some parts of the drainage systems to be below the normal water level and has thus rendered them ineffective.
The minimal discharge to maintain a water level of 1.7 m for navigation (this means 300 m3/s released in the navigation channel from Nakhon Sawan to the Chao Phraya dam, and 80 m3/s downstream of the dam) cannot be maintained because large amounts of water are diverted from the river for dry season irrigation in the northern and central regions. This has reduced the volume of inland waterway transport fivefold between 1978 and 1990. The volumes of water released by the Bhumipol and Sirikit dams are increasingly important to prevent saltwater intrusion, even if they do not meet the navigation demand.
Leptospirosis seems to prevail in flood-prone and irrigation areas, but is under control. There are no clear impacts (positive or negative) of irrigation on health. This is probably the result of a the complicated interaction between socio-economic factors and land use changes. People whose paddy is in irrigation areas are better off economically than those in rainfed areas and hence can afford better health care. Changes in land use transform remote irrigation areas into suburban areas with reasonable road access. As noted above, poverty is less in irrigation areas than in rainfed areas.
During the period 1984-2007 Thailand has 317 513 cases of HIV, resulting in 87 643 deaths. Most HIV cases occur in the services and agriculture sectors in age ranges from 25 to 34 years.
In 1999, the main water-borne diseases were acute diarrhoea (affecting 1.48 percent of the population) dysentery (0.14 percent) and enteric fever (0.03 percent). Malaria, as a water-related disease, affected 0.12 percent of the population.
Water management in agriculture is said to have to focus on improving water-use efficiency. Reasons for this are: (i) the trend indicates that Thailand’s water shortage is emerging; (ii) the agriculture sector consumes the largest proportion of water.
Improving agricultural water-use efficiency must be done through IWRM and must be river basin oriented. To do so, organization and institutional tools must be in place. Organization tools include river Basin Organizations, Apex body and line agencies. Institutional tools include laws, policy and strategies.
In tandem with improving agricultural water-use efficiency, the farmers should move from traditional agriculture to modern agriculture, making use of high technology such as precise water control.
Center for Agricultural Statistics, Ministry of Agriculture and Cooperatives. 2006. Agricultural statistics of Thailand, crop year 2005/06. Bangkok.
ESCAP (United Nations Economic and Social Commission for Asia and the Pacific). 1991. Assessment of water resources and water demand by users sectors in Thailand. New York, USA.
FAO. 1999. Irrigation in Asia in figures. FAO Water Report No. 18. Rome.
Hydrologist Assembly. 2006. Hydrologist Assembly, 11th Year Volume 10-2006 .Bangkok
National Economic and Social Development Board, Office of the Prime Minister. 2001. The ninth national economic and social development plan 2002-2006. Bangkok.
National Economic and Social Development Board, Office of the Prime Minister. 2006. The tenth national economic and social development plan 2007-2011. Bangkok.
National Statistical Office, Office of the Prime Minister. 2006. Statistical yearbook of Thailand. Bangkok.
Thai Hydrologist Assembly. 2007. Journal of Hydrologist Assembly.
World Bank. 1985. Options and Investments priorities in irrigation development.
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