Knowledge (XXG)

Thale Noi Non-Hunting Area

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of extirpation. Smaller populations result in declining genetic diversity of native species in the area, consequently losing their capacity to adapt to changing environmental conditions. Shrimp cultivation in the Songkhla Lake Basin alone rose from ~35 km2 in 1982 to ~78 km in 2000 changing the landscape from fertile wetland habitat to polluted and degraded water and soil resources over time. Clearing of mangrove forests in the protected area has also been reported with a reduction of over 87% land cover which leads to the destabilisation of the shoreline and significant loss of nursery areas for aquatic species. Deforestation of both Melaleuca and mangrove forests bordering Thale Noi lake has increased soil erosion and runoff resulting in extensive sedimentation, that has caused water levels to drop by ~10 cm every year increasing fish mortality.
983: 275:). Thale Luang adjoins Thale Sap (360 km or 140 sq mi) which connects to the southernmost lake, Thale Sap Songkhla (182 km or 70 sq mi) that opens into the Gulf of Thailand through a 380 m wide strait. Approximately 94% (422 km or 163 sq mi) of the reserve is terrestrial and 6% (28 km or 11 sq mi) is aquatic. Thale Noi lake is approximately 5 km wide and 6 km long with an average depth of 1.2 m, however water levels fluctuate significantly with changing seasonal conditions, dropping to around 80 cm in dry season and increasing to a depth of 3 m in some areas during the wet season. 1053: 1064:
sustainable methods of cultivating and harvesting natural resources within the wetlands cause no further loss of biodiversity. Weak enforcement of regulations, lack of coordinated programming and inadequate data collection and record keeping have previously been identified as key issues of concern in the management of this ecosystem, however it is unknown if these problems have been addressed in recent times. Immediate management concerns should focus on preserving biodiversity, improving water quality, preserving fishery resources and resolving social conflicts arising from resource usage in the area.
865: 531: 644: 240:(IUCN) declared it a Protected Area Category III (Natural Monuments), aimed at protecting particular natural features of a small area with high visitor value. The wetlands’ valuable feature is its provision of suitable breeding habitats for tens of thousands of native and migratory bird species. Thale Noi Non-Hunting Area was the first official non-hunting wildlife area declared in Thailand. Furthermore, the Kuan Ki Sian knoll, a 4.94 km area within the non-hunting grounds was declared as a ‘Wetland of International Importance’ in 1998 by the 850: 516: 71: 995: 263: 59: 550:, are harvested extensively for food, medicine and religious ceremonies. Thai people use all parts of this species for myriad uses including the rhizomes, stems, leaves, petals, pods and seeds in cooking; the flowers and leaves for Buddhist rituals; and the leaves, pods, petioles, stamens and pollen for treating a variety of ailments such as sinusitis, diabetes and fever. Similarly, leaves from the Pandanus plant, 1010: 624:), once common in the Thale Noi Non-Hunting Area are facing declining populations due to habitat destruction from land conversion, pollution and over-exploitation in the pet trade. This species is commonly bred in Thailand for the purpose of betting on aggressive fighting male individuals and for their attractive colouring. A secondary threat, as a consequence of the international trade of this species, is 743: 505:, or Grey Sedge, in the Thale Noi region has led to shortages in supply for local communities’ dependent on the plant as a primary source of income. This species is intensely harvested by over 1,000 local families (over 70% of working women), who use the stems for weaving into mats, baskets, bags and other handicraft items for sale. The cultivation of 659: 207:(alternate spelling: Talae or Talay) is a protected fresh water wetland located in Phatthalung province, southern Thailand. Covering an area of 460 km, the wetlands are situated approximately 20 km inland from the east coast peninsula of the Gulf of Thailand and 115 km north of the Malaysian border in 842:
and trapping may also contribute to the declining Fishing Cat population in the region, due to a reduction of food availability and increased risk of being killed by farmers protecting their stock or being sold in the illegal pet trade. A recent study in 2013 found that Fishing Cats in the Thale Noi
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The construction of sluice gates at the northern part of Thale Luang in 1956 ceased the flow of saline water into Thale Noi lake, creating a freshwater biome that had significant impacts on the ecosystem. Reducing or eliminating connectivity between the larger lake system and Thale Noi lake affected
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Thale Noi Non-Hunting Area is internationally recognised for the valuable habitat, breeding grounds and refuge it provides to an extensive variety of indigenous and migratory bird species. Myriad other species of mammals, reptiles, amphibians, fish and other aquatic species also inhabit the wetlands
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Thale Noi Non-Hunting Area experiences tropical monsoonal weather with little variation in average temperatures throughout the year. There are distinct wet and dry seasons experienced on the southern east coast of Thailand with the rainy season running from October to March and dry season from April
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The conversion of wetlands into agricultural and industrial lands is the most significant threat to biodiversity in Thailand. Habitat destruction, fragmentation, pollution and overexploitation of the Thale Noi Non-Hunting Area has reduced populations of flora and fauna species with continuing risks
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Thale Noi Non-Hunting Area is part of the greater Songkhla Lake Basin, the largest lagoon lake in Thailand, covering an area of over 8,000 km (3,100 sq mi) in its entirety. The lake joins with Thale Luang, a 473 km (183 sq mi) basin, via 3 channels – Khlong Naang Riam,
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The Thai name ‘Thale Noi’ translates to ‘little sea’ in English language (thale = sea; noi = little). The wetlands were internationally recognised as a biodiversity hotspot in 1975 when the Department of National Parks, Wildlife & Flora, under the Ministry of National Resources and Environment
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Thale Noi Non-Hunting Area provides habitat and breeding grounds for over 180 native and migratory bird species that use the wetlands all year round or on their annual migratory journeys. Research linking bird distributions to changing ecological conditions show that bird behaviour is an important
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for its diversity of flora and fauna species, its value as a breeding haven for myriad bird species and for the presence of vulnerable and endangered species inhabiting the area. The wetlands are presently governed by the Royal Forestry Department who work with local authorities and communities to
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are considered ‘bioindicators’ of wetland ecosystems, therefore declining populations within Thale Noi are concerning and indicates deteriorating ecological conditions that threatens the biodiversity of the entire ecosystem. The most significant threat to these species are the loss of habitat and
1071:, particularly on wetlands, is steadily increasing, changing rainfall patterns, increasing storm frequency and intensity, impacting all levels of biological and ecological systems. Dedicated management strategies are required to address these issues and the impact on Thale Noi Non-Hunting Area. 1063:
Freshwater wetlands are particularly vulnerable to human activities due to their disproportionate abundance of flora and fauna in both terrestrial and aquatic areas for refuge and habitat. Education, training and enforcement of environmental protection laws needs to be more effective to ensure
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swamp forests to floating aquatic macrophytes and microscopic phytoplankton. Records from the late 1990s show there were 72 species of flora within the protected area of Thale Noi, however more recent studies reveal dramatic reductions in plant populations with only 25 species remaining in the
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Eutrophication has been recorded in areas close to human settlements as a consequence of pollutants entering the wetlands from households and industry. Unaware or unconcerned with the impacts of environmental degradation on the ecosystem, runoff from rubber and food production industries and
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There are mixed reports to the number of fish species found in Thale Noi Lake with some ranging from 45 species to other much lower figures of 26 species. It is likely that many species have been lost from the wetlands due to habitat conversion, pollution and fragmentation resulting from
758: 914:) farmed by approximately 280 families in the Thale Noi Non-Hunting Area. It is unknown what impact the numbers of buffalo have on the ecosystem, however many avian species use their grazing areas for feeding and breeding sites including heron, egrets, stilts and wader species. 1027:) populations inhabit the reserve year round as one of only two breeding locations within Thailand and remain constant throughout the year. Cormorants, waders, herons, egrets, crakes, bitterns, terns, grebe and kites are among other avian species found in the non-hunting area. 976:) populations are also in decline due to habitat destruction, degradation and fragmentation, currently listed by the IUCN as Near Threatened, however large populations continue to breed in the wetlands between April and July, with over 20,000 individuals recorded in May 2002. 565:
providing valuable ecosystem services to local communities and as part of the greater food web. Many species in the wetlands have been declared as Vulnerable, Endangered or Critically Endangered by the IUCN and are listed on their Red List of Threatened Species
730:), both of which are also listed on CITES due to trade exploitation. Populations of these species have declined in Thailand due to extensive habitat loss from land conversion into rice fields, rubber tree plantations and shrimp farms. The Four-toed Terrapin ( 1040:
the feeding and breeding cycles of fish and other aquatic fauna which consequently impacted the entire food web. Reports of increased weed infestation has also been documented as a result of limited salt-water intrusions that previously reduced populations.
962:) is classified as Near Threatened. These species have all experienced rapid population declines due to land conversion for agriculture and industry causing habitat loss and environmental pollution that some species exhibit sensitivities to. Painted Stork ( 364:) species bordering both ends of the reserve represent the largest Melaleuca habitat in Thailand. These flood tolerant trees provide protective breeding grounds throughout the year for common native waterbird species such as the Little Cormorant ( 779:) are both IUCN listed as Least Concern, however are protected in Thailand under the Wild Animal Reservation & Protection Act (WARPA). All other reptile species are classified as Least Concern and include: Elephant Trunk Snake ( 628:
resulting from privately bred stock being released into wild areas. This loss of genetic diversity increases the risk of local extinctions as populations become less adapted to survive in changing environments. It is reported that
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Current records indicate that populations of all amphibians within the protected area are not threatened, however this is likely due to lack of available data. Amphibian species present in the reserve are: Black-spectacled Toad
1930: 556:, found within the reserve are commonly used throughout Thailand for flavouring dishes and adding natural green colouring to drinks and sweets, as well as being used as a traditional medicine for treating diabetes. 271:
Khlong Ban Klang and Khlong Yuan, however sluice gates were installed in 1956 by the Royal Irrigation Department to prevent salt water intrusion to create freshwater conditions conducive to rice production (see
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forests dominate the north and south with extensive rice paddy fields to the east and remaining areas combine swamp marsh, grassland and sedge beds, with only a relatively small area of open water.
1356:"Songkhla Lake: the Largest Natural Lake in Thailand - See more at: http://www.eosnap.com/image-of-the-day/songkhla-lake-the-largest-natural-lake-in-thailand-march-30th-2009/#sthash.SHvlQev7.dpuf" 633:, Walking Catfish, native to Thailand were previously found at Thale Noi, however there is no recent literature available on the distribution of this species in the area. The Giant Sword Minnow ( 1763: 478:
spp.) and myriad other Phytoplankton species. Many macrophyte populations form dense floating patches on the lake surface providing refuge and habitat for both mobile and sessile organisms.
956:) is Vulnerable, although it was once the most abundant species of stalk but now may also be extirpated from Thailand due to no recent documented sightings; and the Spot-billed Pelican ( 982: 1060:
Thale Noi Non-Hunting Area provides an array of valuable ecosystem services to local communities whose economy revolves almost explicitly around exploiting the lake's resources.
1947: 1188: 736:), a semi-aquatic species that lives in terrestrial and freshwater habitats, was once found in the Thale Noi Non-Hunting Area, however is now Extinct in the Wild in Thailand,. 1299:"Application of integrated environmental management through the preparation of an environmental action programme: Case study from the Songkhla Lake Basin in southern Thailand" 1341:
Iwasaki, S. & Shaw, R., [doi:10.3850/S179392402009000106 "Human Security and Coping Brackish Environmental Hazards in Fishing Communities of Songkhla Lake, Thailand"],
1820:"A New Subspecies Identification and Population Study of the Asian Small-Clawed Otter (Aonyx cinereus) in Malay Peninsula and Southern Thailand Based on Fecal DNA Method" 211:. Thale Noi Non-Hunting Area is one of the largest natural freshwater lakes in South East Asia. It is the smallest, northernmost basin in the chain of lagoons that form 415:) which all contribute to ecosystem stability for maintaining soil composition, food sources, sanctuary and breeding grounds for both terrestrial and aquatic species. 696:
There are 25 recorded species of reptiles in the Thale Noi Non-Hunting Area with 4 species listed on the IUCN Red List as Vulnerable: the Southeast Asian Box Turtle (
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in the Thale Noi Non-Hunting Area does not require legal land tenure and little financial outlay, making it an attractive method of earning income for poor families.
944:), classified as Critically Endangered and may be extirpated from the Thale Noi area and from Thailand, however data is lacking on this species; the Masked Finfoot ( 968:), is classified as Near Threatened, have been recorded at the site in the past (Parr 1994), however it is now on the verge of extinction in Thailand. Similarly, 237: 864: 643: 102: 347:
is due to the heavy impact human populations have had on the area through the over-exploitation of natural resources and pollution into the lake (see
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Thale Noi Non-Hunting Area is a biologically diverse wetland with multiple habitat types supporting a vast array of flora and fauna species. Dense
849: 658: 2024: 1259: 1355: 481:
Thale Noi Non-Hunting Area hosts several orchid species that are protected by the Convention on International Trade in Endangered Species (
637:) was once also found in Thale Noi Non-Hunting Area however is now extirpated due to its sensitivities to pollution and gillnet fishing. 515: 1237: 418:
Herbaceous macrophytes present in the reserve also provide important habitats for birds, otters and other wildlife and include reeds (
1185: 2019: 1524:"Change detection and identification of land potential for planting Krajood (Lepironia articulata ) in Thale Noi, Southern Thailand" 1445: 878:
Other mammal species found within the protected area are classified as Least Concern by the IUCN include the Crab-eating Macaque (
994: 44: 1502:"The Effect of Fishing on the Distribution and Behaviour of Waterbirds in the Kukut area of Lake Songkla, Southern Thailand" 388:
forests also provides night roosting areas for migratory bird species from April to July, such as the Black-headed Ibis (
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Other non-threatened aquatic species present in the wetlands include several economically valuable species - Snakehead (
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There are 10 recorded species of mammals inhabiting the Thale Noi Non-Hunting Area. The Asian Small-Clawed Otter (
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Mukherjee, S., Sanderson, J., Duckworth, W., Melisch, R., Khan, J., Wilting, A., Sunarto, S. & Howard, J.G.,
1068: 742: 1764:"Species Diversity, Distribution and Proposed Status of Monitor Lizards (Family Varanidae) in Southern Thailand" 618:
and industrialisation, however more research is required to quantify the extent of loss. Siamese Fighting Fish (
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Non-Hunting Area were almost completely nocturnal, making recording individual numbers difficult to establish.
835: 825: 552: 958: 615: 1220: 1418: 964: 952: 1910: 1890: 1870: 1523: 1603: 1780: 1709: 1676: 1479: 1044:
surrounding pig, shrimp and crop farms are additional sources of pollution contaminating the area.
946: 935:) species have shown to correlate with average temperatures, relative humidity and total rainfall. 880: 722: 485:) due to historical over-exploitation for their aesthetic appeal, including Finlayson's Cymbidium ( 216: 1802: 1726: 1627: 1221:"Population of Waterbirds in the Breeding Colony at Khuan Khi Sian, Thailand's First Ramsar Site" 716: 372:), as well as other common avian species with annual breeding cycles including the Little Egret ( 360: 1746: 70: 1619: 1462: 1093: 969: 698: 344: 262: 241: 220: 163: 1931:"The Expansion of Inland Shrimp Farming and Its Environmental Impacts in Songkla Lake Basin" 1611: 704: 546: 58: 48: 1948:"Rural male leadership, religion and the environment in Thailand's mid-south, 1920s–1960s" 1431: 1192: 910: 625: 620: 807:) and several species of common terrestrial and water snakes, skinks and garden lizards. 1607: 1276: 938:
Globally threatened avian species listed on the IUCN Red List include: Baer's Pochard (
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to September; November being the wettest month of the year and July being the driest.
2008: 1501: 838:
due to land conversion into rice paddies and shrimp farms (Mukherjees et al. 2010).
732: 720:). Two species are currently listed as Endangered - the Yellow-headed Temple Turtle ( 395:
Other water adapted plant species found in the area include common mangrove species (
212: 1631: 940: 1854:"Distribution of Resident Birds in a Protected Tropical Habitat in South Thailand" 1540: 839: 1615: 219:, Phatthalung and Songkhla provinces and is home to the critically endangered 1623: 117: 104: 1590: 1569:
Meksuwan, P., Pholpunthin, P., Walsh, E.J., Segers, H. and Wallace, R., ,
1819: 1662:
Monvises, A., Nuangsaeng, B., Sriwattanarothai, N. and Panijpan, B., ,
1411:"A Socio-Economic and Tourism Assessment at Thale Noi Non-Hunting Area" 823:) are both on the IUCN Red List as Vulnerable species and Fishing Cat ( 1588:
La-ongsri, Woranuch; Trisonthi, Chusie; Balslev, Henrik (2009-08-01).
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The 2 monitor species present in the wetlands, the Clouded Monitor (
1410: 1088: 1051: 482: 261: 1929:
Tanavud, C. Yongchalermchai, C., Bennui, A. and Kasetsart, O.D.,
1837:"Terrestrial Activity Patterns of Wild Cats from Camera Trapping" 1591:"Management and use of Nelumbo nucifera Gaertn. in Thai wetlands" 1858:
International Society for Southeast Asian Agricultural Sciences
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biological indicator of change. Populations of Cattle Egret (
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Sunrise boat trips to see blooming lotus at Thale Noi lake.
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Wright, L., de Silva, P., Chan, B. & Reza Lubis, I.,
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Wakte, K.V., Nadaf, A.B., Ratnakar, J. and Jawali, N., ,
1089:"Kuan Ki Sian of the Thale Noi Non-Hunting Area Wetlands" 1768:
The Natural History Journal of Chulalongkorn University
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The Natural History Journal of Chulalongkorn University
684:), Swamp eel (Fluta alba), 2 freshwater prawn species ( 493:) both found on limestone outcrops within the reserve. 174:
Kuan Ki Sian of the Thale Noi Non-Hunting Area Wetlands
18:
Kuan Ki Sian of the Thale Noi Non-hunting Area Wetlands
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Office of the National Environment Board of Thailand
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Wunbua, J., Nakhapakorn, K. and Jirakajohnkool, S.,
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Asian Journal of Environment and Disaster Management
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Macrobrachium lanchesteri, Macrobrachium rosenbergii
215:, spreading across three provincial boundaries into 1966:Cookey, P.E., Darnswasdi, R. and Ratanachai, C., , 1463:"Important Bird and Biodiversity Areas - Thale Noi" 186: 178: 170: 161: 157: 149: 141: 133: 96: 88: 80: 32: 1589: 1528:Songklanakarin Journal of Science & Technology 1171:Cookey, P., Darnswasdi, R. & Ratanchai, C., , 680:); several catfish varieties; Grey Featherback ( 1303:Lakes & Reservoirs: Research and Management 1219:Kaewdee, W., Thirakhupt, K. and Tunhikorn, S., 238:International Union for Conservation of Nature 1583: 1581: 1579: 1254: 1252: 1250: 1215: 1213: 1211: 1209: 1207: 1205: 8: 1293: 1291: 1289: 950:) is Endangered; the Lesser Adjutant Stork ( 1658: 1656: 1654: 1518: 1516: 1514: 1496: 1494: 1492: 908:). There are also over 4000 Water Buffalo ( 714:) and the Southeast Asia Softshell Turtle ( 1962: 1960: 1905: 1903: 1885: 1883: 1500:Pierce, G.J., Spray, C.J. and Stuart, E., 1404: 1402: 1400: 1398: 1396: 1394: 1392: 1390: 1388: 1151: 1149: 1147: 1145: 1143: 1141: 348: 272: 29: 1741: 1739: 1386: 1384: 1382: 1380: 1378: 1376: 1374: 1372: 1370: 1368: 1321: 1319: 1317: 1315: 1313: 1311: 1167: 1165: 1056:Houses of National Park on Thale Noi lake 1980: 1978: 1976: 1797: 1795: 1793: 1691: 1689: 1337: 1335: 1114: 1112: 284: 1925: 1923: 1446:"A Study of the Waterfowl at Thale Noi" 1080: 988:Birds taking flight over Thale Noi lake 978: 845: 738: 639: 511: 1427: 1416: 1023:Non-threatened species, Purple Heron ( 601:) and the Malaysian Narrowmouth Toad ( 1762:Lauprasert, K. & Thirakhupt, K., 1480:"Forest inventory at Thale Noi Basin" 1450:Natural History Bulletin Siam Society 829:) is presently listed as Endangered. 392:), an IUCN Near Threatened species. 185: 177: 169: 160: 145:29 April 1975 Ramsar Site 13 May 1998 7: 1646:Genetic Resources and Crop Evolution 1571:International Review of Hydrobiology 79: 1852:Rittiboon, K. & Karntanut, W., 1708:Vidthayanon, C. & Allen, D.J., 27:Protected area in southern Thailand 1952:Journal of Southeast Asian Studies 726:) and the Yellow-headed Tortoise ( 581:); Pointed-tongued Floating Frog ( 376:), the Black-crowned Night Heron ( 25: 1297:Chufamanee, P. and Lonholdt, L., 1260:"Phatthalung Tourism Information" 489:) and the Aloe-leafed Cymbidium ( 137:460 km (180 sq mi) 1556:Ecological Research Division, , 1275:Thai Meteorological Department, 1157:Emerald Group Publishing Limited 1008: 993: 981: 863: 848: 819:) and the Smooth-coated Otter ( 756: 741: 702:); the Giant Asian Pond Turtle ( 657: 642: 529: 514: 69: 57: 1986:Cambridge Philosophical Society 1841:The Raffles Bulletin of Zoology 1695:Humphrey, S. & Bain, J., , 1596:Wetlands Ecology and Management 1236:Ramsar Convention Secretariat, 775:) and the Asian Water Monitor ( 140: 87: 1710:"Macrochirichthys macrochirus" 1281:Thai Meteorological Department 1186:"Protected Areas Category III" 1175:, 2016. Retrieved 05-05-2016 . 1173:Ocean & Coastal Management 1155:Iwasaki, S. & Shaw, R., , 927:), Black-crowned Night Heron ( 84:Phatthalung Province, Thailand 1: 2025:Non-hunting areas of Thailand 1988:, 2006. Retrieved 01-05-2016. 1970:, 2016. Retrieved 05-05-2016. 1954:, 2011. Retrieved 01-05-2016. 1937:, 2001. Retrieved 01-05-2016. 1917:, 2012. Retrieved 05-05-2016. 1897:, 2013. Retrieved 05-05-2016. 1877:, 2015. Retrieved 05-05-2016. 1860:, 2011. Retrieved 05-05-2016. 1843:, 2013. Retrieved 01-05-2016. 1826:, 2014. Retrieved 05-05-2016. 1809:, 2010. Retrieved 01-05-2016. 1787:, 2015. Retrieved 01-05-2016. 1770:, 2001. Retrieved 05-05-2016. 1753:, 2000. Retrieved 05-05-2016. 1733:, 2000. Retrieved 05-05-2016. 1716:, 2013. Retrieved 05-05-2016. 1683:, 2013. Retrieved 05-05-2016. 1666:, 2009. Retrieved 05-05-2016. 1648:, 2009. Retrieved 01-05-2016. 1573:, 2014. Retrieved 01-05-2016. 1560:, 1981. Retrieved 01-05-2016. 1547:, 2012. Retrieved 01-05-2016. 1541:"Threskiornis melanocephalus" 1530:, 2012. Retrieved 01-05-2016. 1508:, 1993. Retrieved 01-05-2016. 1486:, 1999. Retrieved 14-05-2016. 1469:, 2016. Retrieved 19-05-2016. 1452:, 1977. Retrieved 01-05-2016. 1362:, 2009. Retrieved 01-05-2016. 1345:, 2009. Retrieved 01-05-2016. 1305:, 2001. Retrieved 01-05-2016. 1283:, 2014. Retrieved 19-05-2016. 1266:, 2016. Retrieved 05-05-2016. 1244:, 2013. Retrieved 01-05-2016. 1242:Ramsar Convention Secretariat 1227:, 2002. Retrieved 05-05-2016. 1199:, 2014. Retrieved 05-05-2016. 1159:, 2010. Retrieved 05-05-2016. 1135:, 2013. Retrieved 05-05-2016. 1122:, 2000. Retrieved 05-05-2016. 688:) and several crab species. 1824:The Scientific World Journal 1745:Asian Turtle Working Group, 1725:Asian Turtle Working Group, 803:); Puff-faced Water Snake ( 711:Siebenrockiella crassicollis 666:Macrochirichthys macrochirus 635:Macrochirichthys macrochirus 497:Economically valuable plants 384:). The thick foliage of the 236:and in conjunction with the 933:Threskiornis melanocephalus 904:); and the Polynesian Rat ( 708:); the Black Marsh Turtle ( 593:); White-lipped Tree Frog ( 390:Threskiornis melanocephalus 49:natural monument or feature 38:Thale Noi Waterfowl Reserve 2041: 1935:Journal of Natural Science 1327:Taylor & Francis Group 900:); Greater Bandicoot Rat ( 890:Paradoxurus hermaphroditus 884:); Malayan Horseshoe Bat ( 205:Thale Noi Non-Hunting Area 33:Thale Noi Non-Hunting Area 1803:"Prionailurus viverrinus" 1616:10.1007/s11273-008-9106-6 1277:"The Climate of Thailand" 1096:Sites Information Service 931:) and Black-headed Ibis ( 855:Asian Small-clawed Otter 795:); Striped Water Snake ( 411:) and the Shore Eugenia ( 198: 194: 153:Royal Forestry Department 68: 56: 42: 37: 2020:Ramsar sites in Thailand 1909:Birdlife International, 1889:Birdlife International, 1869:Birdlife International, 1697:The Sandhill Crane Press 1539:Birdlife International, 1461:Birdlife International, 1120:Nordic Journal of Botany 1069:impact of climate change 836:population fragmentation 487:Cymbidium finlaysonianum 380:) and the Cattle Egret ( 1911:"Mycteria leucocephala" 1891:"Leptoptilos javanicus" 1506:Biological Conservation 1258:Royal Thai Government, 1238:"Ramsar Sites Criteria" 872:Prionailurus viverrinus 826:Prionailurus viverrinus 783:); Reticulated Python ( 676:spp.); Climbing Perch ( 597:); Burmese Squat Frog ( 595:Polypedates leucomystax 553:Pandanus amaryllifolius 544:Royal or Sacred lotus, 466:); Golden Bladderwort ( 358:) and the White Samet ( 354:The Weeping Paperbark ( 338:Plant life ranges from 1984:Dudgeon, D. et al., , 1835:Lynam, A. J., et al., 1818:Rosli, M.K.A. et al., 1467:Birdlife International 1426:Cite journal requires 1131:Ponnampalam et al., , 1057: 959:Pelecanus philippensis 896:); Plantain Squirrel ( 888:); Common Palm Civit ( 799:); Rice Paddy Snake ( 649:Siamese Fighting Fish 616:agricultural expansion 585:); Common Green Frog ( 472:Ceratophyllum demersum 440:Paspalum scrobiculatum 356:Melaleuca leucadendron 310:Swamp/Sedge/Grassland 267: 1727:"Heosemys annandalii" 1264:Royal Thai Government 1055: 1031:Environmental Threats 965:Mycteria leucocephala 953:Leptoptilos javanicus 929:Nycticorax nycticorax 886:Rhinolophus malayanus 781:Acrochordus javanicus 682:Notopterus notopterus 589:); Chinese Bullfrog ( 501:Over-exploitation of 446:spp.); Sacred Lotus ( 442:) and other grasses ( 413:Syzygium antisepticum 401:Sonneratia caseolaris 378:Nycticorax nycticorax 349:Environmental Threats 273:Environmental Threats 265: 225:Orcaella brevirostris 118:7.76667°N 100.15306°E 75:Thale Noi Locator Map 898:Callosciurus notatus 892:); Jarvan Mongoose ( 728:Indotestudo elongate 609:Fish & Shellfish 523:Lepironia articulata 507:Lepironia articulata 503:Lepironia articulata 491:Cymbidium aloifolium 462:); Asian Watermoss ( 458:); Water Snowflake ( 436:Lepironia articulata 397:Rhizophora apiculate 368:) and Purple Heron ( 345:loss of biodiversity 245:manage the reserve. 1608:2009WetEM..17..279L 1478:Liangphonphan, S., 1017:Heliopais personata 947:Heliopais personata 894:Herpestes javanicus 881:Macaca fascicularis 821:Lutra perspicillata 791:); Monocled Cobra ( 723:Hieremys annandalii 631:Prophagorus niuhofi 599:Calluella guttulata 434:spp.); Grey Sedge ( 430:spp.); Spike-rush ( 409:Alstonia spathulata 366:Phalocrocorax niger 327:11 sq mi 316:42 sq mi 305:59 sq mi 294:66 sq mi 217:Nakhon Si Thammarat 150:Governing body 114: /  1191:2014-08-04 at the 1118:Coesel, P.F.M., , 1058: 805:Homalopsis buccata 789:Bungarus fasciatus 785:Python reticulatus 717:Amyda cartilaginea 678:Anabas testudineus 579:Bufo melanostictus 464:Salvinia cucullata 407:); Siamese Balsa ( 403:); the Nipa Palm ( 361:Melaleuca cajuputi 288:Melaleuca forests 268: 258:Ecosystem dynamics 187:Reference no. 123:7.76667; 100.15306 2015:IUCN Category III 1968:Hydrology Journal 1946:Reynolds, C. J., 1677:"Betta splendens" 1675:Vidthayanon, C., 974:T. melanocephalus 970:Black-headed Ibis 797:Enhydris enhydris 787:); Banded Krait ( 773:Varanus nebulosus 765:Cuora amboinensis 763:Asian Box Turtle 699:Cuora amboinensis 587:Hylarana erythrae 468:Utricularia aurea 460:Nymphoides indica 456:Nymphaea nouchali 331: 330: 242:Ramsar Convention 221:Irrawaddy dolphin 202: 201: 89:Nearest city 16:(Redirected from 2032: 1989: 1982: 1971: 1964: 1955: 1944: 1938: 1927: 1918: 1907: 1898: 1887: 1878: 1867: 1861: 1850: 1844: 1833: 1827: 1816: 1810: 1799: 1788: 1781:"Aonyx cinereus" 1777: 1771: 1760: 1754: 1743: 1734: 1723: 1717: 1706: 1700: 1693: 1684: 1673: 1667: 1660: 1649: 1642: 1636: 1635: 1593: 1585: 1574: 1567: 1561: 1554: 1548: 1537: 1531: 1520: 1509: 1498: 1487: 1476: 1470: 1459: 1453: 1442: 1436: 1435: 1429: 1424: 1422: 1414: 1406: 1363: 1354:Earth Snapshot, 1352: 1346: 1339: 1330: 1323: 1306: 1295: 1284: 1273: 1267: 1256: 1245: 1234: 1228: 1217: 1200: 1182: 1176: 1169: 1160: 1153: 1136: 1129: 1123: 1116: 1107: 1106: 1104: 1102: 1085: 1015:tMasked Finfoot 1012: 997: 985: 902:Bandicota indica 867: 852: 801:Enhydris plumbea 777:Varanus salvator 760: 745: 705:Heosemys grandis 661: 646: 547:Nelumbo nucifera 538:Nelumbo nucifera 533: 518: 474:); Green Algae ( 450:); White Lotus ( 448:Nelumbo nucifera 374:Egretta garzetta 285: 129: 128: 126: 125: 124: 119: 115: 112: 111: 110: 107: 73: 61: 30: 21: 2040: 2039: 2035: 2034: 2033: 2031: 2030: 2029: 2005: 2004: 1993: 1992: 1983: 1974: 1965: 1958: 1945: 1941: 1928: 1921: 1908: 1901: 1888: 1881: 1868: 1864: 1851: 1847: 1834: 1830: 1817: 1813: 1800: 1791: 1778: 1774: 1761: 1757: 1747:"Batagur baska" 1744: 1737: 1724: 1720: 1707: 1703: 1694: 1687: 1674: 1670: 1661: 1652: 1643: 1639: 1587: 1586: 1577: 1568: 1564: 1555: 1551: 1538: 1534: 1521: 1512: 1499: 1490: 1477: 1473: 1460: 1456: 1443: 1439: 1425: 1415: 1408: 1407: 1366: 1353: 1349: 1340: 1333: 1324: 1309: 1296: 1287: 1274: 1270: 1257: 1248: 1235: 1231: 1218: 1203: 1193:Wayback Machine 1183: 1179: 1170: 1163: 1154: 1139: 1133:Aquatic Mammals 1130: 1126: 1117: 1110: 1100: 1098: 1087: 1086: 1082: 1077: 1050: 1033: 1019: 1013: 1004: 1000:Baer's Pochard 998: 989: 986: 920: 911:Bubalus bubalis 874: 868: 859: 853: 813: 767: 761: 752: 748:River terrapin 746: 694: 668: 662: 653: 651:Betta splendens 647: 626:genetic erosion 621:Betta splendens 611: 603:Kaloula pulchra 583:Occidozyga lima 574: 562: 540: 534: 525: 519: 499: 454:); Blue lotus ( 438:); Rice Grass ( 426:spp.), rushes ( 422:spp.); sedges ( 336: 260: 251: 233: 166: 122: 120: 116: 113: 108: 105: 103: 101: 100: 76: 64: 52: 28: 23: 22: 15: 12: 11: 5: 2038: 2036: 2028: 2027: 2022: 2017: 2007: 2006: 2003: 2002: 2000: 1998: 1996: 1991: 1990: 1972: 1956: 1939: 1919: 1899: 1879: 1871:"Aythya baeri" 1862: 1845: 1828: 1811: 1789: 1772: 1755: 1735: 1718: 1701: 1685: 1668: 1650: 1637: 1602:(4): 279–289. 1575: 1562: 1549: 1532: 1510: 1488: 1471: 1454: 1444:Storer, P.J., 1437: 1428:|journal= 1364: 1347: 1331: 1307: 1285: 1268: 1246: 1229: 1201: 1177: 1161: 1137: 1124: 1108: 1079: 1078: 1076: 1073: 1049: 1046: 1032: 1029: 1025:Ardea purpurea 1021: 1020: 1014: 1007: 1005: 999: 992: 990: 987: 980: 919: 916: 906:Rattus exulans 876: 875: 869: 862: 860: 854: 847: 812: 809: 769: 768: 762: 755: 753: 747: 740: 693: 690: 670: 669: 663: 656: 654: 648: 641: 610: 607: 573: 570: 561: 558: 542: 541: 535: 528: 526: 520: 513: 498: 495: 452:Nymphaea lotus 405:Nypa fruticans 370:Ardea purpurea 343:reserve. This 335: 332: 329: 328: 325: 322: 318: 317: 314: 311: 307: 306: 303: 300: 296: 295: 292: 289: 259: 256: 250: 247: 232: 229: 209:Satun province 200: 199: 196: 195: 192: 191: 188: 184: 183: 180: 176: 175: 172: 168: 167: 164:Ramsar Wetland 162: 159: 158: 155: 154: 151: 147: 146: 143: 139: 138: 135: 131: 130: 98: 94: 93: 90: 86: 85: 82: 78: 77: 74: 66: 65: 62: 54: 53: 43: 40: 39: 35: 34: 26: 24: 14: 13: 10: 9: 6: 4: 3: 2: 2037: 2026: 2023: 2021: 2018: 2016: 2013: 2012: 2010: 2001: 1999: 1997: 1995: 1994: 1987: 1981: 1979: 1977: 1973: 1969: 1963: 1961: 1957: 1953: 1949: 1943: 1940: 1936: 1932: 1926: 1924: 1920: 1916: 1915:IUCN Red List 1912: 1906: 1904: 1900: 1896: 1895:IUCN Red List 1892: 1886: 1884: 1880: 1876: 1875:IUCN Red List 1872: 1866: 1863: 1859: 1855: 1849: 1846: 1842: 1838: 1832: 1829: 1825: 1821: 1815: 1812: 1808: 1807:IUCN Red List 1804: 1798: 1796: 1794: 1790: 1786: 1785:IUCN Red List 1782: 1776: 1773: 1769: 1765: 1759: 1756: 1752: 1751:IUCN Red List 1748: 1742: 1740: 1736: 1732: 1731:IUCN Red List 1728: 1722: 1719: 1715: 1714:IUCN Red List 1711: 1705: 1702: 1698: 1692: 1690: 1686: 1682: 1681:IUCN Red List 1678: 1672: 1669: 1665: 1659: 1657: 1655: 1651: 1647: 1641: 1638: 1633: 1629: 1625: 1621: 1617: 1613: 1609: 1605: 1601: 1597: 1592: 1584: 1582: 1580: 1576: 1572: 1566: 1563: 1559: 1553: 1550: 1546: 1545:IUCN Red List 1542: 1536: 1533: 1529: 1525: 1519: 1517: 1515: 1511: 1507: 1503: 1497: 1495: 1493: 1489: 1485: 1481: 1475: 1472: 1468: 1464: 1458: 1455: 1451: 1447: 1441: 1438: 1433: 1420: 1412: 1405: 1403: 1401: 1399: 1397: 1395: 1393: 1391: 1389: 1387: 1385: 1383: 1381: 1379: 1377: 1375: 1373: 1371: 1369: 1365: 1361: 1357: 1351: 1348: 1344: 1338: 1336: 1332: 1328: 1322: 1320: 1318: 1316: 1314: 1312: 1308: 1304: 1300: 1294: 1292: 1290: 1286: 1282: 1278: 1272: 1269: 1265: 1261: 1255: 1253: 1251: 1247: 1243: 1239: 1233: 1230: 1226: 1222: 1216: 1214: 1212: 1210: 1208: 1206: 1202: 1198: 1194: 1190: 1187: 1181: 1178: 1174: 1168: 1166: 1162: 1158: 1152: 1150: 1148: 1146: 1144: 1142: 1138: 1134: 1128: 1125: 1121: 1115: 1113: 1109: 1097: 1095: 1090: 1084: 1081: 1074: 1072: 1070: 1065: 1061: 1054: 1047: 1045: 1041: 1037: 1030: 1028: 1026: 1018: 1011: 1006: 1003: 996: 991: 984: 979: 977: 975: 971: 967: 966: 961: 960: 955: 954: 949: 948: 943: 942: 936: 934: 930: 926: 925:Bubulcus ibis 917: 915: 913: 912: 907: 903: 899: 895: 891: 887: 883: 882: 873: 866: 861: 858: 857:Aonyx cinerea 851: 846: 844: 841: 837: 832: 831:Aonyx cinerea 828: 827: 822: 818: 817:Aonyx cinerea 810: 808: 806: 802: 798: 794: 793:Naja kaouthia 790: 786: 782: 778: 774: 766: 759: 754: 751: 750:Batagur baska 744: 739: 737: 735: 734: 733:Batagur baska 729: 725: 724: 719: 718: 713: 712: 707: 706: 701: 700: 691: 689: 687: 683: 679: 675: 667: 664:Sword Minnow 660: 655: 652: 645: 640: 638: 636: 632: 627: 623: 622: 617: 608: 606: 604: 600: 596: 592: 591:Rana rugulosa 588: 584: 580: 571: 569: 567: 559: 557: 555: 554: 549: 548: 539: 532: 527: 524: 517: 512: 510: 508: 504: 496: 494: 492: 488: 484: 479: 477: 473: 470:); Hornwort ( 469: 465: 461: 457: 453: 449: 445: 441: 437: 433: 429: 425: 421: 416: 414: 410: 406: 402: 398: 393: 391: 387: 383: 382:Bubulcus ibis 379: 375: 371: 367: 363: 362: 357: 352: 350: 346: 341: 333: 326: 323: 320: 319: 315: 312: 309: 308: 304: 301: 299:Rice Paddies 298: 297: 293: 290: 287: 286: 283: 281: 276: 274: 264: 257: 255: 248: 246: 243: 239: 230: 228: 226: 222: 218: 214: 213:Songkhla Lake 210: 206: 197: 193: 189: 181: 173: 171:Official name 165: 156: 152: 148: 144: 136: 132: 127: 99: 95: 91: 83: 72: 67: 60: 55: 50: 46: 45:IUCN category 41: 36: 31: 19: 1985: 1967: 1951: 1942: 1934: 1914: 1894: 1874: 1865: 1857: 1848: 1840: 1831: 1823: 1814: 1806: 1784: 1775: 1767: 1758: 1750: 1730: 1721: 1713: 1704: 1696: 1680: 1671: 1664:Science Asia 1663: 1645: 1640: 1599: 1595: 1570: 1565: 1557: 1552: 1544: 1535: 1527: 1505: 1483: 1474: 1466: 1457: 1449: 1440: 1419:cite journal 1409:Parr, John. 1359: 1350: 1342: 1326: 1325:King, V., , 1302: 1280: 1271: 1263: 1241: 1232: 1224: 1196: 1180: 1172: 1156: 1132: 1127: 1119: 1099:. Retrieved 1092: 1083: 1066: 1062: 1059: 1042: 1038: 1034: 1024: 1022: 1016: 1002:Aythya baeri 1001: 973: 963: 957: 951: 945: 941:Aythya baeri 939: 937: 932: 928: 924: 921: 909: 905: 901: 897: 893: 889: 885: 879: 877: 871: 870:Fishing Cat 856: 830: 824: 820: 816: 814: 804: 800: 796: 792: 788: 784: 780: 776: 772: 770: 764: 749: 731: 727: 721: 715: 709: 703: 697: 695: 685: 681: 677: 673: 671: 665: 650: 634: 630: 619: 612: 602: 598: 594: 590: 586: 582: 578: 575: 563: 551: 545: 543: 537: 536:Royal Lotus 522: 506: 502: 500: 490: 486: 480: 475: 471: 467: 463: 459: 455: 451: 447: 443: 439: 435: 431: 427: 423: 419: 417: 412: 408: 404: 400: 396: 394: 389: 385: 381: 377: 373: 369: 365: 359: 355: 353: 339: 337: 313:109 km 302:153 km 291:170 km 279: 277: 269: 252: 234: 224: 204: 203: 840:Overfishing 521:Grey Sedge 324:28 km 321:Open water 182:13 May 1998 142:Established 121: / 109:100°09′11″E 97:Coordinates 92:Phatthalung 2009:Categories 1075:References 1048:Management 572:Amphibians 432:Eleocharis 420:Phragmites 179:Designated 1624:1572-9834 386:Melaleuca 340:Melaleuca 280:Melaleuca 106:7°46′00″N 63:Thale Noi 1632:25530088 1189:Archived 1101:25 April 692:Reptiles 81:Location 1699:, 1990. 1604:Bibcode 1329:, 1998. 811:Mammals 444:Scleria 428:Scirpus 424:Cyperus 249:Climate 231:History 1630:  1622:  1360:Chelys 1184:IUCN, 1094:Ramsar 674:Channa 1628:S2CID 1484:AGRIS 918:Birds 560:Fauna 483:CITES 476:Chara 334:Flora 47:III ( 1620:ISSN 1432:help 1197:IUCN 1103:2018 1067:The 399:and 134:Area 1612:doi 605:). 351:). 227:). 190:948 2011:: 1975:^ 1959:^ 1950:, 1933:, 1922:^ 1913:, 1902:^ 1893:, 1882:^ 1873:, 1856:, 1839:, 1822:, 1805:, 1792:^ 1783:, 1766:, 1749:, 1738:^ 1729:, 1712:, 1688:^ 1679:, 1653:^ 1626:. 1618:. 1610:. 1600:17 1598:. 1594:. 1578:^ 1543:, 1526:, 1513:^ 1504:, 1491:^ 1482:, 1465:, 1448:, 1423:: 1421:}} 1417:{{ 1367:^ 1358:, 1334:^ 1310:^ 1301:, 1288:^ 1279:, 1262:, 1249:^ 1240:, 1223:, 1204:^ 1195:, 1164:^ 1140:^ 1111:^ 1091:. 568:. 1634:. 1614:: 1606:: 1434:) 1430:( 1413:. 1105:. 972:( 577:( 223:( 51:) 20:)

Index

Kuan Ki Sian of the Thale Noi Non-hunting Area Wetlands
IUCN category
natural monument or feature

Thale Noi Thailand World Map
7°46′00″N 100°09′11″E / 7.76667°N 100.15306°E / 7.76667; 100.15306
Ramsar Wetland
Satun province
Songkhla Lake
Nakhon Si Thammarat
Irrawaddy dolphin
International Union for Conservation of Nature
Ramsar Convention

Environmental Threats
loss of biodiversity
Environmental Threats
Melaleuca cajuputi
CITES
Grey Sedge Lepironia articulata
Royal Lotus Nelumbo nucifera
Nelumbo nucifera
Pandanus amaryllifolius

agricultural expansion
Betta splendens
genetic erosion
Siamese Fighting Fish Betta splendens
Sword Minnow Macrochirichthys macrochirus
Cuora amboinensis

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