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"  # % & $ ' ) * + , - . / 0 1 2 3  4  5  6  7  8 9 : ; < = > ? @ A B C D E F G H I J ~!~"~#~$~%~&~'~(~)~ *~ +~ ,~ -~ .~/~0~1~2~3~4~5~~ ~ (~3KhsU7 c 9  e - f < X t J  kMeG) @~T tJ xN$Bp+ Y  YL@ ! gH@! gBA Data Form].[39 Code]8 gF@! gL@! gP@! gL@! gP@! g [IBA Data Form].[17 Ownership]= gH@! g[IBA Data Form].[15 Map]7 gB@! gB@! g\@! g\@! g\@! g\@! g\@! g \@! g D@! g BA Data Form].[11 Area]8 g h@! g f@! g[IBA Data Form].[8 Country]: gV@ ! gL@ ! gD@ ! gL@ ! g[IBA Data Form].[2 Date]7 g[IBA Data Form].[1 Compiler]; g![IBA Data Form].[Serial number]> gIBA Data Form+++  G G  GThreats Table+++   G  GSpecies Table+++   G  GIBA Data FormSpecies Tablej@ !QE+  BA Data Form].[11 Area]8 g f@! g L@! g L@! g[IBA Data Form].[2 Date]7 g"[Species Table].[31 Criteria A4]? g"[Species Table].[31 Criteria A3]? g"[Species Table].[31 Criteria A2]? g"[Species Table].[31 Criteria A1]? gB@! g[Species Table].[23 Species]; g[Species Table].[Serial ID]: gSpecies Table+++ IBA Data Form+++   GIBA Data FormAdditional Info Tablez@!aU+ f@! gL@! gL@! gL@! gAdditional Info Table;;; IBA Data Form+++   GIBA Data FormSpecies Tablej@.QE+  ![IBA Data Form].[Serial number]> g "[Species Table].[31 Criteria A4]? g "[Species Table].[31 Criteria A3]? g "[Species Table].[31 Criteria A2]? gLVAL-h< b F  ` N : &Z n"HL8<V @ @ @ @ @ @ @ @ @ @[IBA Data Form].[54 Person/Organization][IBA Data Form].[53 Details of campeign][IBA Data Form].[52 Type of action][IBA Data Form].[51 Person/Organization][IBA Data Form].[48 Relationship to IBA][IBA Data Form].[47 Central Coordinates Lon 3][IBA Data Form].[47 Central Coordinates Lon 2][IBA Data Form].[47 Central Coordinates Lon 1][IBA Data Form].[47 Central Coordinates Lat 3][IBA Data Form].[47 Central Coordinates Lat 2][IBA Data Form].[47 Central Coordinates Lat 1][IBA Data Form].[45 IUCN category][IBA Data Form].[42 Full Name of Site][IBA Data Form].[41 Political Units][IBA Data Form].[22 Criteria Notes][IBA Data Form].[21 Criteria Proposed][IBA Data Form].[20 Biome Code Proposed][IBA Data Form].[19 EBA Code Proposed][IBA Data Form].[18 General Description][IBA Data Form].[16 Management Plan][IBA Data Form].[14 Altitude Max][IBA Data Form].[14 Altitude Min][IBA Data Form].[13 Central Coordinates Lon 3][IBA Data Form].[13 Central Coordinates Lon 2][IBA Data Form].[13 Central Coordinates Lon 1][IBA Data Form].[13 Central Coordinates Lat 3][IBA Data Form].[13 Central Coordinates Lat 2][IBA Data Form].[13 Central Coordinates Lat 1][IBA Data Form].[12 Area Accuracy][IBA Data Form].[10 Administrative Region (Level 2)][IBA Data Form].[9 Administrative Region (Level 1)][IBA Data Form].[7 International Site Name][IBA Data Form].[6 National Site Name][IBA Data Form].[5 Final IBA Code][IBA Data Form].[4 Temporary IBA Code][IBA Data Form].[Serial number] =[Species Table].[ID][IBA Data Form].[9 Administrative Region (Level 1)][IBA Data Form].[6 National Site Name][IBA Data Form].[4 Temporary IBA Code][Species Table].[23 English Name][IBA Data Form].[Serial number] =[Additional Info Table].[ID][IBA Data Form].[9 Administrative Region (Level 1)][IBA Data Form].[6 National Site Name][IBA Data Form].[4 Temporary IBA Code][Additional Info Table].[63-2 Threats] Y(HlHkN##((((((Y  Y t Y n Y c Y e Y 3 Y uIDD60 Additional information on birds<61 Other important Fauna/FloraB62 Research/Conservation Projects*63-1 Habitat/Land Use63-2 ThreatsT64 Lobbying or campeigning for legislation#4kkk#5kkk#YkYZYYL{797EE06F-4561-11D5-865B-00D0B78F5836}IDPrimaryKey####### # # # # #}~~~~      !#$"%'(&)+,*-/012345678 9:.;=>?@ABCD<EGHIJKLMNOP Q         F                                ! "  # % $e].[Serial ID]: gSpecies Table+++ IBA Data Form+++   GIBA Data FormAdditional Info Tablez@!aU+ f@! gL@! gL@! gL@! gAdditional Info Table;;; IBA Data Form+++   GIBA Data FormSpecies Tablej@.QE+  ![IBA Data Form].[Serial number]> g "[Species Table].[31 Criteria A4]? g "[Species Table].[31 Criteria A3]? g "[Species Table].[31 Criteria A2]? g; v1b N  : k @ @ @ @ @ @ @ @ @ @ @ @ @ @ @ @ @ @vCvAwDwFwGwExHxJxKxIyLyNyOyMzPzRzSzTzUzVzWzXzQ{Y{[{\{Z|]|_||^}}}}~~~~      !#$"%'(&)+,*-/012345678 9:.;=>?@ABCD<EGHIJKLMNOP Q         F                                  @@@LVAL1  Combo12d Ctl58_Results_of_lobbying_or_campeign_Label58 Results of lobbying or campeign_LabelmText0Serial IDID52 Type of action58 Results of lobying campeignHuman settlement within the IBA is largely restricted to Memong town, with little settlement outside of this area. Commercial hunting is a particular threat to populations of large mammals but is less of a threat to bird populations, but for the notable exception of Green Peafowl, which is specifically Human settlement within the IBA is largely restricted to Memong town, with little settlement outside of this area. Commercial hunting is a particular threat to populations of large mammals but is less of a threat to bird populations, but for the notable exception of Green Peafowl, which is specifically targeted due to its value in the wildlife trade.. In addition, subsistence hunting of smaller species is currently low. The major potential future threat to biodiversity at the IBA is planned and unplanned human in-migration, and the agricultural expansion and increase in hunting that would accompany it.There are numerous permanent human settlements within the IBA, some large, including the provincial town of Tbeng Meanchey, the district town of Chom Khsan, and Phum Takang (a resettlement village), which was established in 1999. For at least the last two years, local people from this village have collected eggs and chicks from the Darter colony within the IBA. All large waterbirds breeding at the IBA face similar, hunting-based threats, especially the ground-nesting Sarus Crane, for which there is a high demand from the wildlife trade in Thailand. Major potential future threats to biodiversity at the IBA include human in-migration, provincial road development plans, and the agricultural expansion and increase in hunting that would accompany it.The mangrove along the western side of the estuary has been significantly reduced by land reclamation and conversion to rice agriculture, as part of a major development project involving the construction and restoration of dykes. Although the mangrove along the eastern side of the estuary is in a better condition, some areas in the south-east have been converted to aquaculture. Upriver, much of the Melaleuca and mangrove has been cut for poles and charcoal production.There has been extensive cutting of the mature mangrove forest at the IBA, particularly for charcoal production. Establishment and expansion of aquacultural ponds has also contributed significantly to loss of mangrove forest. In addition, there is some hunting of shorebirds at the IBA, primarily by the local Cham (ethnic muslim) communities.Much of the forest within the IBA has been degraded to some extent by logging, and collection of bamboo and other non-timber forest products. Illegal commercial timber extraction is estimated to have affected 80% of Bokor National Park. As well as habitat degradation, habitat loss is also a serious threat to biodiversity at the IBA, with local people clearing forest for agriculture. Another serious threat is hunting, particularly the widespread use of ground snares. Species such as Chestnut-headed Partridge, Green Peafowl and hornbills have been seen for sale at a wildlife market on Road No. 4. However, enforcement activities aimed at reducing hunting are currently being implemented with some success.One of the major threats to biodiversity at the IBA is habitat loss, particularly clearance of mangrove. In addition, hunting is a serious problem in the neighbouring Ream National Park, although the severity of this threat within the IBA has not been assessed.LVAL V a  Timmins and Men Soriyun (in pre.) recorded prints probably from Gaur (Bos saurus) (Vulnerable) in 1998. Neth Neath et al. (2001) A Tiger Survey of Lomphat Wildlife Sanctuary: Asiatic Jackal, Dhole, Asiatic Black Bear, Sun Bear, Jungle CatTimmins and Men Soriyun (in pre.) recorded prints probably from Gaur (Bos saurus) (Vulnerable) in 1998. Neth Neath et al. (2001) A Tiger Survey of Lomphat Wildlife Sanctuary: Asiatic Jackal, Dhole, Asiatic Black Bear, Sun Bear, Jungle Cat, Leopard Cat, Fishing Cat, Asian Golden Cat, Leopard, Tiger. They alsso recorded the following red listed Chelonians, Yellow-headed Temple Turtle (Hieremus annandalii) (Vulnerable) and Elongated Tortoise (Indotestudo elogata) (Vulnerable).Timmins and Men Soriyun (in prep.) recorded Long tailed Macaque (Macaca fascicularis) Near- threatened, and Otter sp. Possible Smooth-Coated (Lutra perspicillata) Vulnerable. Baird (1997) reported Irrawaddy Dolphin (Orcaella brevirostris) (data deficient) to have much declined, documenting only a population of 2-5 animals near the confluence with the Sre Pok River. The following red listed fish species presumably occur: Probarbus jullieni, P. labeamajor, Pangasius sanitwongsei, and possibly Pangasianodon gigas. (Rainboth 1996).Irrawaddy Dolphin (Orcaella brevirostris) (data deficient) has undergone severe decline estimated now 10-15 animals bewteen Stung Treng and Lao border (Baird and Bounhong 1994, Baird 1997). The following red listed fish species occur Probarbus jullieni, P. labeanmajor, Pangasianodon gigas, Pangasius saritwongsei. All have declined in recent years (Rainboth 1996, Roberts and Baird 1995). Davies (1994) records the botanical communities of the sandy island of the middle river as being unique and therefore of great value.The specific survey combined with all other sources recorded a total of 186 bird species at the site. Apart from the Globally Threatened Sarus Crane, a further eight Globally Threatened and six Globally Near Threatened bird species have been recorded. In addition, 28 bird species of regional conservation concern occur at the site. Elogated Tortoise (Indotestudo elongata) and Malayan Snail-eating Turtle (Malayemys subtrijuga) are collected by villagers from March-May and from June-July. Smooth-coated Otter, Common Palm Civet and Leopard Cat occur in that area as well but they are rare.Siamese Crocodile (Crocodylus siamensis) known to occur at Moat Khla, but local people reperted that now is very rare. IUCN category - critically endangered. The flooded forest is extremely important for many fish species (Rainboth 1996). The flooded forest represents and important and unique botanical community (McDonald et al. 1997).Siamese Crocodile (Crocodylus siamensis) occurs in the area (critical endangered). Also Long tailed Macaque (Macaca fascicularis) near threatened. Extremely important for many fish species (Ramboth 1996). Important botanical community (McDonald et al. 1997). Turtle populations little known but said to be decreasing.Long tailed Macaque (Mamaca fascicularis) occurs in the mangrove. The best, most mature mangrove forest in Cambodia and arguably in the whole of Indochina and the gulf of Thailand.Very important for large animals: Tiger, Elephant, Sun Bear, Leopard, Leopard Cat, Black Bear, Pileated Gibbon (Hylobates pileatus), Marbled Cat, Hog Deer, Pig-tailed Macaque, Long-tailed Macaque, Pangolin and otter spp. Most of which are Red Listed. The largest area in Cabodia for Pinus Merkisii, Cambodia's only Pine species.Indo-Pacific Humpback Dolphin (Sousa chinensis) occurs around Koh Thmei and is data deficient.5LVAL32  7jQe!Eight Woodpecker species and two nuthatch species are found together in the pure pine forest. Wreathed Hornbill occuEight Woodpecker species and two nuthatch species are found together in the pure pine forest. Wreathed Hornbill occurs in the important flocks outside the breeding season and the first record for the country of the GNT Brown Hornbill.50 Baya Weavers, 278 Grey Herons and 25 Purple Herons were recorded in November 2001.During the survey, 43 nests of Oriental Darter were observed on 14 November 2001.Other regionally significant bird species: Alexandrine Parakeet, Woolly-necked Stork, Great Slaty Woodpecker.Other regionally significant bird species: Great Slaty Woodpecker, Streak-throated Woodpecker, White-bellied Woodpecker, Oriental Pied Hornbill, Stork-billed Kingfisher, Alexandrine Parakeet, Green Imperial Pigeon, Orange-breasted Green Pigeon, Woolly-necked Stork, Grey Heron.Other region sinificant birds species recorded : German's Peacock Pheasant, Blue-eared Kingfisher, Black-backed Kingfisher, Hodgson's Hawk Cuckoo, Violet Cuckoo, Pompadour Green Pigion, Jerdon' s Baza, Mountain Hawk Eagle, Malayan Night Heron, Blue-rump Pitta,Blue and White Flycatcher, Blue-throated Flycatcher, Yellow-bellied Warbler, Black-throated Laughingthrush, Purple-naped Sunbird, Streaked Spiderhunter, Pin-tailed Parrofinch.Other regionally significant birds species occur in the site such as Asian Openbill, Wooly -necked Stork, Brahminy Kite, Blak-shouldered Kite,Creasted Serpent Eagle, Grey -headed Fish-Eagle, Sport-billed Duck and Comb Duck.Other regionally significant bird species : Little Cormorant, Indian Cormorant, Grey Heron, Purple Heron, Woolly-necked Stork, Black-necked Stork, Cotton Pygmy-goose, Brahminy Kite, White-bellied Sea-Eagle, Great-thick Knee, River Tern, Little Tern, Orange-breasted Green Pigeon, Green Imperial Pigeon, Alexandrine Parakeet, Pied Kingfisher, Streak-throated Woodpecker, Great Slaty Woodpecker, Yellow Crown Woodpecker, Broad-and-red Broadbill, White-bellied Woodpecker.Other regionally significant bird species recorded: Woolly-necked Stork (at least 22 birds, May 1998 (Timmins and Men Soriyun in prep.), Green Imperial Pigeon, Oriange-breasted Green Pigeon, Alexandrine Parakeet, Streak-throated Woodpecker, Great Slaty Woodpecker, Golden crested Myna.Other regionally significant birds recorded: Grey Heron, Purple Heron, Woolly-necked Stork, Cotton Pygmy-goose, Brahminy Kite, Great Thick-knee (13 recorded in May-June 1998 by Timmins and Men Soriyun in prep.), River Tern (47 recorded by Timmins and Men Soriyun in prep. In May-June 1998), Green Imperial Pigeon, Alexandrine Parakeet, Pied Kingfisher (36 recorded by Timmins and Men Soriyun in prep. May-June 1998), Golden crested Myna, Great Slaty Woodpecker, Black Eagle.Other regionally significant species present: Little Cormorant, Indian Cormorant, Grey Heron, Brahminy Kite, White bellied sea Eagle, River Lapwing, Small Pratincole, Great Thick Knee, River Tern, Green imperial Pigeon, Alexandrine Parakeet, Pied Kingfisher, Baya Weaver.Woolly-necked Stork and Comb Duck were also reported.One Comb Duck recorded by Mundkur in March 1998 and 12 in June 1998. Sarus Cranes are only present in the dry season and leave the site to breeding areas elsewhere with the onset of rains in June. Also Grey Heron, Purple Heron, Brahminy Kite, Baya Weaver.Other regionally significant birds (Probably all breeding). Great Cormorant, Grey Heron, Purple Heron, Glossy Ibis, Cotton Pygmy Goose, Comb Duck, Watercock and Baya Weaver.A large numbers of redshank and greenshank, and smaller numbers of Egret sp. And Pond Heros were found feeding as well as 42 Great Crested Terns roosting on a mudflat.3649 waders of 17 species recorded in January 1996.Other regionally sinificant bird species: Woolly-necked Stork."([ L ` % Q . r C  p A  z K  lsxmCtl33_34C_Sea_cliffs_and_rocky_shores33-34C Sea cliffs and rocky shoresjCtl33_34P_Rock_stacks_and_islands33-34P Rock stacks and islandsd Ctl33_34P_Rock_stacks_and_islandsx33-34P Rock stacks and islandsxmCtl33_34C_Rock_stacks_and_islands33-34C Rock stacks and islandsjCtl33_34P_Inland_cliffs_and_rocky_slopes33-34P Inland cliffs and rocky slopesd Ctl33_34P_Inland_cliffs_and_rocky_slopesx33-34P Inland cliffs and rocky slopesxmCtl33_34C_Inland_cliffs_and_rocky_slopes33-34C Inland cliffs and rocky slopesjCtl33_34P_Scree_and_boulders33-34P Scree and bouldersd Ctl33_34P_Scree_and_bouldersx33-34P Scree and bouldersxmCtl33_34C_Scree_and_boulders33-34C Scree and bouldersjCtl33_34P_Caves33-34P Cavesd Ctl33_34P_Cavesx33-34P CavesxmCtl33_34C_Caves33-34C CavesjCtl33_34P_Arable_land33-34P Arable landd Ctl33_34P_Arable_landx33-34P Arable landxmCtl33_34C_Arable_land33-34C Arable landjCtl33_34P_Rice_paddies33-34P Rice paddiesd Ctl33_34P_Rice_paddiesx33-34P Rice paddiesxmCtl33_34C_Rice_paddies33-34C Rice paddiesjCtl33_34P_Improved_pasture_land33-34P Improved pasture landd Ctl33_34P_Improved_pasture_landx33-34P Improved pasture landxmCtl33_34C_Improved_pasture_land33-34C Improved pasture landjCtl33_34P_Perennial_crops__orchards_and_groves33-34P Perennial crops, orchards and grovesd Ctl33_34P_Perennial_crops__orchards_and_grovesx33-34P Perennial crops, orchards and grovesxmCtl33_34C_Perennial_crops__orchards_and_groves33-34C Perennial crops, orchards and grovesjCtl33_34P_Forestry_and_agro_industrial_plantations33-34P Forestry and agro-industrial plantationsd Ctl33_34P_Forestry_and_agro_industrial_plantationsx33-34P Forestry and agro-industrial plantationsxmCtl33_34C_Forestry_and_agro_industrial_plantations33-34C F.@.2@3#-@3!,r@.@3#+@.+@3#)1@3#&@.@0#%8@.@0#$ @0!#@+@0%"H@0!!Y@0! a@.@/#@/!m@/!@/!@.u@/#@.o@+e@/**'$@.@-#@&@(@-**3@-!W@&=@-#S@&@-#c@$!o@ &@$#@ &@+@,**'@ & @++@,**'@ &@,#@ &@+@)**'@&@%@***' @&@%@***' @& @%J@(H@*66*7 7@&@*#@&Q@%{@)**'(@)!S@%I@(@)**5@&?@%@)**'@&G@(@$**35@&@%Y@$**'J@%@$%@@&`@%@$**'LVALp&, industrialjCtl35_36P_Small_settlements35-36P Small settlementsd Ctl35_36P_Small_settlementsx35-36P Small settlementsxmCtl35_36C_Small_settlements35-36C Small settlementsjCtl35_36P_Watershed_management35-36P Watershed managementd Ctl35_36P_Watershed_managementx35-36P Watershed managementxm Ctl35_36C_Watershed_management35-36C Watershed managementj!Ctl35_36P_Other35-36P Otherd "Ctl35_36P_Otherx35-36P Otherxm#Ctl35_36C_Other35-36C Otherj$Ctl35_36P_Not_utilized35-36P Not utilizedd %Ctl35_36P_Not_utilizedx35-36P Not utilizedxm&Ctl35_36C_Not_utilized35-36C Not utilizedj'Ctl35_36P_Unknown35-36P Unknownd (Ctl35_36P_Unknownx35-36P Unknownxm)Ctl35_36C_Unknown35-36C Unknownd *x54d +x55d ,x56-tH_tb__tH[tb^[ͬ'X~yaE[зX6DetailmCtl41_Political_Units41 Political Unitsd Ctl41_Political_Units08=Babc&e ghHi_ j*k5jL9k@(Protected Area Table Ariald2 Tahomahgh Tahomam45 Tahomao2 Tahoma` Detail{C+C).nm57U`aXb i $41 Political Units$41 Political Units Arial*Ctl41_Political_UnitsC+C).nd5U`a<bcd 041 Political Units0 x9 $41 Political Units Arial6Ctl41_Political_Units0 x9 C+C).nm57U`aXbi k(42 Full Name of Site(42 Full Name of Site Arial.Ctl42_Full_Name_of_SiteC+C).nd5U`a<bcd 442 Full Name of Site0 x9 (42 Full Name of Site Arial:Ctl42_Full_Name_of_Site0 x9 C+C).nm57U`!aTbi k43 Year43 Year ArialCtl43_YearC+C).nd5U`!brcd 43 Year0 x9 43 Year Arial Ctl43_Year0 x9 C+C).nm57U`<ab i k44 Designation44 Designation Arial"Ctl44_DesignationC+C).nd5U`<abacd (44 Designation0 x9 44 Designation Arial.Ctl44_Designation0 x9 C+C).nm57U`aRbi k46 Area46 Area ArialCtl46_AreaC+C).nd5U`}abcd 46 Area0 x9 46 Area Arial Ctl46_Area0 x9 C+C).nm57U`9ab:i k847 Central Coordinates Lat 1847 Central Coordinates Lon 1 Arial>Ctl47_Central_Coordinates_Lat_1CThe main habitat degradation in the dry season is fires which are widspread and intensive over all the pine forest. FamiliaThe main habitat degradation in the dry season is fires which are widspread and intensive over all the pine forest. Familial scale logging is the livelihood of the majority of the families living in Tayang commune. Hunting still occurs in the Park.River forest (tropical) is not included in habitat classification types.Seasonally inundated forest is included in habitat type classification.Seasonally inundated forest is not avaible in habitat classification.LVALe t Lal_Coordinates_Lon_1C+C).nd5U` ab cd D48 Central Coordinates Lon 10 x9 847 CentrAlthough there are few villages within the IBA, villagers living in adjacent areas continue to hunt, fish, gather forest products and engage in shifting cultivation within the IBA. Of these activities, hunting is a perhaps the most severe tAlthough there are few villages within the IBA, villagers living in adjacent areas continue to hunt, fish, gather forest products and engage in shifting cultivation within the IBA. Of these activities, hunting is a perhaps the most severe threat to biodiversity. This activity is a particular threat to populations of ground birds, such as Green Peafowl, which are susceptible to snaring and egg collection. Commercial logging has already affected substantial areas within the IBA.Prior to the establishment of the Sarus Crane Conservation Area in February 2000, local people used to regularly hunt cranes using poison. In 1999, the main driving force behind this was a high demand from the wildlife trade in Thailand. Hunting of Sarus Cranes has now been largely curtailed through enforcement and awareness activities, although small-scale hunting of other species for food still occurs. Currently, the most significant threat is probably conversion of seasonally inundated grassland and open woodland to agriculture. A potential long-term threat may be the manipulation of water levels for irrigation downstream.One of the major threats to biodiversity at the IBA is habitat loss, from both legal and illegal logging, particularly as this activity reduces the number of large trees suitable for hole-nesting species, such as White-winged Duck. In addition, hunting is rife throughout the area, and a particular problem is hunting with dogs, which is a severe threat to flightless, molting White-winged Ducks during in the wet season. A further, although less severe, threat is disturbance caused by resin collectors, who travel and camp along rivers and streams.Over-exploitation is the biggest threat to biodiversity at the IBA. There are two floating villages within the IBA, and local people hunt birds and collect eggs and chicks opportunistically while engaged in fishing and other activities. These activities are a particular threat to birds that breed at the IBA. Additional threats to biodiversity at the IBA include cutting of trees for firewood and clearance of forest for agriculture, although the impacts of these threats are currently limited.Collection of eggs and chicks at the nest remains the single most threat to the continued survival of colonial waterbirds on the Tonle Sap. Teams of large waterbird collectors target breeding colonies of cormorants, pelicans, storks and ibises for egg and chick collection and organise several trips into the flooded forest during the breeding season. The intervention of government officials and international conservation teams, and the establishment of the Prek Toal Environmental station have significantly improved the situation in this vital breeding site since 1997. Collection undertaken by Tonle Sap people (fishermen) has been significantly reduced, but it is reportedly still conducted by farmers moving to the lake from upland areas in Battambang Province. Aside from fish, the main income derived from the natural resources of the inundated forest is firewood. Firewood collection for local cooking consumption is believed to be sustainable as the flooded forest vegetation is remarkably resilient, resprouting very rapidly after cutting. However, particular targeting of large trees may adversely affect availability of nesting sites for the large waterbirds.LVAL  DetOne of the major threats to biodiversity at the IBA is hunting, which is a particular threat to populations of large mammal species and large-bodied birds, such as Sarus Crane and Green Peafowl. In surrounding areas, outside of the IBA, habitat degradation and loss, due to commercial logging and conversion of seasonal meadows to agriculture, is an ongoing concern. While these activities are currenly very limited within the IBA, the potential for them to increase exiOne of the major threats to biodiversity at the IBA is hunting, which is a particular threat to populations of large mammal species and large-bodied birds, such as Sarus Crane and Green Peafowl. In surrounding areas, outside of the IBA, habitat degradation and loss, due to commercial logging and conversion of seasonal meadows to agriculture, is an ongoing concern. While these activities are currenly very limited within the IBA, the potential for them to increase exists. Along the Srepok River, cutting of trees and clearance of forest for agriculture is leading to degradation and loss of riverine forest, while destructive fishing methods, particularly the use of poisons and explosives is also of concern. However, the major threats to riverine birds are probably hunting, egg collection and disturbance due to human activities on sandbanks. A potential future threat is the development of major hydropower schemes on the Srepok River.Major threats to biodiversity at the IBA include hunting and, more importantly, egg collection and disturbance due to human activities on sandbars, which is likely to negatively affect the breeding success of sandbar-nesting birds. Another threat is posed by degradation and loss of riverine forest, due to cutting of trees and clearance of land for agriculture. A further major threat comes from the existing and planned development of hydropower schemes upstream in Vietnam. There is some evidence that the changes in flow regimes due to existing hydropower dams are already negatively affecting nesting riverine birds, by both sudden flash floods destroying nests and changes in the process of sedimentation leading to a reduction in the availability of nesting sites.Perhaps the most severe threats to the riverine bird community that have operated at the IBA to date are hunting, egg collection and disturbance due to human activities on sandbanks during the breeding season. Other major threats are cutting of trees and clearance of land for agriculture along the banks of the river. Illegal fishing, particularly the use of poison and explosives is also a cause for concern. A potential future threat with potentially catastrophic impacts is the development of major hydropower or navigation schemes on the Mekong River or its larger tributaries.Hunting of water birds and Bengal Florican, chiefly by poisoning and trapping, is an ongoing threat; much of this is for sale in local markets. In the wet season, local people also apparently catch large waterbirds by using fish-hooks. A more recent threat which is of major concern is the extensive conversion of grasslands to deepwater rice in southeastern Banteay Meanchey and western Siem Reap Provinces. This is rapidly reducing available breeding habitat for Bengal Florican. Associated disturbance from agricultural activities (e.g. ploughing) and grazing of large herds of domestic livestock probably further reduces Bengal Florican breeding success. Children use catapults to scare or kill birds when they are in the fields with their cattle. LVAL=4 (  l r  oSVbNp5bcr35cd z452bci j l r  oSVbN{2425bcJ d  l r  oSVbN`  tH[ wb_[ tH_ wb__ d5U678"`bXce 23 Species0 x9 23 Species ArialDetachedLabel&Ctl23_Species0 x9 d5U678"`Sbwce24 Season0 x9 24 Season ArialDetachedLabel$Ctl24_Season0 x9 d5]678"`cbce$26 Abundance0 x9 26 Abundance ArialDetachedLabel*Ctl26_Abundance0 x9 d5W678"`sbsce"31 Criteria0 x9 31 Criteria ArialDetachedLabel(Ctl31_Criteria0 x9 d5U678"`Dbcce32 Notes0 x9 32 Notes ArialDetachedLabel"Ctl32_Notes0 x9 d5U68"`'bceLabel39Pop min Ariald5U68"`S+bc eLabel40max Ariald5U68"`/bc eLabel41accracy Ariald5U68"`4bc eLabel42Year Ariald5U68"`7bceLabel43Pop trend Ariald5U68"`s>bc eLabel44Trend acc Ariald5U678"` brceLabel4623 English Name ArialDetachedLabel 5Byja ;``m7U:<"`aZbe 23 Species23 Species ArialCtl23_Speciesm 27U:<"`DaZbw cve k32 NotesMr Kri Vana reported that he saw a Tiger 25 km to the west of Siem Pang town in 1995, while he was in the forest extracting timber. From the description given, it was impossible to determine with certainty whether the report referred to Tiger or Leopard (Panthera pardus). The two local rangers reported that the commonest lMr Kri Vana reported that he saw a Tiger 25 km to the west of Siem Pang town in 1995, while he was in the forest extracting timber. From the description given, it was impossible to determine with certainty whether the report referred to Tiger or Leopard (Panthera pardus). The two local rangers reported that the commonest large mammals in western Siem Pang district were Sambar (Cervus unicolor) and Indian Muntjac (Muntiacus muntjak). Another species reported to be present in western Siem Pang district was Dhole (Cuon alpinus). However, both informants reported that there were no Asian Elephant (Elephas maximus) in western Siem Pang district.Some other regionally significant mammal species also occur in the IBA like Dhole (Cuon alpinus), Fishing CatRed listed mammals occuring (all from Prum Sovanna, mammal list in Preah Vihea province): Asian Elephant, Leopard, Guar, Banteng, Eld's Deer, Dhole, Tiger.Four pictures of Tigers were taken by Camera trape in coupe 2a. This is the first time that the species has been photographed in the wild in Cambodia. Ten pictures of Sun bear were obtainted from just coupe 2a in Keo Sema Samling forest Concession, Mondulkiri province,Cambodia. A Gaur photo-trapped along a concession road in logged forest. Banteng were taken at two mineral licks. Siamese Crocodile (Crocodylus siamensis) (IUCN critically endangered): Long tailed Macaque (Macaca fascicularis) (IUCN-Near threatened).Other regionally significant mammal and primate species also occur in the area such as Tiger, Leopard, Dhole, Golden Cat, Marbled Cat, Clouded Leopard, Sambar, Sun Bear, and Pig-tailed Macaque.LVAL 1d ehn"";"";"";"";"10";"2"#37-38I ExtHunting is only occurring at low levels, primarily for subsistence, and, although it is thought to be potentially increasing, it is not currently a severe threat to populations of large waterbirds. Perhaps the greatest threat to these populations is opportunistic collection of eggs and chicks from the nest, particularly in the case of Sarus Crane. Local people close to the international border with Laos report that poison, which is used to catch fish in permanentHunting is only occurring at low levels, primarily for subsistence, and, although it is thought to be potentially increasing, it is not currently a severe threat to populations of large waterbirds. Perhaps the greatest threat to these populations is opportunistic collection of eggs and chicks from the nest, particularly in the case of Sarus Crane. Local people close to the international border with Laos report that poison, which is used to catch fish in permanent pools and streams, can also kill waterbirds. Dynamite fishing is also reported to be an increasing problem at seasonal pools. Another significant threat to biodiversity at the IBA is illegal logging in areas of semi-evergreen forest, particularly along watercourses. Major potential future threats to biodiversity at the IBA include human in-migration, provincial road development plans, and the agricultural expansion and increase in hunting that would accompany it.One of the major threats to biodiversity at the IBA is hunting with guns and snares. Hunting is a particular threat to Green Peafowl, which is specifically targeted due to its value in the wildlife trade. Recently, the level of hunting at the IBA has begun to decline, as a result of conservation interventions. Another major threat to biodiversity is logging. Although official logging activities have been restricted to certain areas in recent times, illegal logging also takes place, and much of the IBA has been logged in the past, in some places quite heavily, leading to localised erosion. Soils suitable for agriculture are distributed throughout large areas of the IBA. Already there is evidence of localised clearance of forest for agriculture, and, in the future, the rate of clearance may increase.Although there is no permanent human settlement within the seasonally inundated area, a number of villages and associated rice paddies are situated at the limit of the inundation zone. During the dry season, as floodwaters recede, large numbers of people move into the inundation zone, from a radius of over 50 km away, to fish, harvest grasses, gather brushwood and wetland plants, and graze domestic livestock in herds that can number several hundred animals. This causes high levels of disturbance throughout large areas of the IBA. Deepwater rice is cultivated annually in the eastern and northern parts of the IBA. During this period, much of the area is ploughed by tractor, which presents a serious threat to nesting Bengal Floricans, in the form of disturbance and nest destruction. A potential future threat is further conversion of grassland areas to deepwater rice cultivation. Another major threat to biodiversity at the IBA is hunting for both food and trade, which affects all waterbirds in the area, and also the Bengal Florican. Hunting has almost certainly accounted for a major decline in florican numbers in the recent past. However, conservation interventions over the last two years appear to have significantly reduced hunting levels in the IBA.+LVAL GCb c*37-38P Intensified forest managementxIntensified forest managementArial-Ctl37_38P_Intensified_forest_managementxj2]`abi#*37-38P Introduction of exotic plan species*37-38P Introduction of exotic pPerhaps the major threat to biodiversity at the IBA is conversion of natural habitat to agriculture. Significant parts of the Melaleuca swamp have already been converted to agriculture, and the wetlands within the swamp appear to be a particular focus for Perhaps the major threat to biodiversity at the IBA is conversion of natural habitat to agriculture. Significant parts of the Melaleuca swamp have already been converted to agriculture, and the wetlands within the swamp appear to be a particular focus for conversion. This is a particular threat to Sarus Crane, which is dependent upon seasonally inundated grasslands. In addition, cutting of Melaleuca, and, to a lesser (nonetheless significant) extent, mangrove, is taking place for pole and charcoal production.Almost all areas of natural habitat within the IBA have been degraded to some extent by former and on-going human activities. A road was built to the summit of Kirirom during the French colonial period and holiday resorts and a tea plantation were established there. The semi-evergreen forest within the IBA has been severely affected by commercial timber extraction, both legal and illegal. Hunting is another threat to biodiversity at the IBA, and has resulted in the eradication of a number of species, including Green Peafowl Pavo muticus and Great Hornbill Buceros bicornis. Furthermore, the forest around the edges of the IBA is being encroached by illegal settlers, who convert forest to agricultural land.One of the major threats to biodiversity at the IBA is illegal logging, with logging roads being constructed into the IBA from Thailand. As well as the direct impact of logging in terms of habitat degradation, the construction of roads is facilitating access to the area by returning refugees, and, as a result, increasing the rate of conversion of forest to agriculture, particularly in lowland areas. The construction of roads also facilitates hunting, much of it is for local consumption and linked with the collection of agarwood (from Aquilaria sp.). However, hunting for commercial purposes, particularly from Thailand, is also thought to be increasing.One of the major on-going threats to biodiversity at the IBA, is the use of poison to hunt waterbirds, which is a particular threat to Sarus Crane. Fishing activities, which are widespread within the IBA, are also a source of threats to biodiversity, particularly the practice of pumping water out of wetlands. Perhaps the greatest threat to biodiversity at the IBA is agricultural expansion. Already, large areas of the floodplain of the Bassac River have been converted to irrigated rice agriculture, and there exist plans to further develop irrigation schemes within the IBA, which would directly threaten the feeding areas of Sarus Crane. However, following realisation of the biodiversity and socio-economic values of the natural habitats at the IBA, these plans are currently being revised to mitigate impacts on the IBA.The major threats to biodiversity at the IBA are hunting and egg collection. These activities are usually conducted opportunistically by local people, whose main occupation is fishing. When local people encounter a nest site, eggs or chicks will be collected, regardless of species or stage of development. In October 2001, local people collected around 500 Darter eggs from within the IBA. Additional threats to biodiversity including cutting of trees for firewood, and, in areas of higher elevation, clearance of forest for agriculture.3LVAL  / A M S l r  oSVbNp5bcr35cd z452bci j l r  oSVbN{2425bcJ d  l r  oSVbN`  tH[ wb_[ tH_ wb__ d5U678"`bXce 23 Species0 x9 23 Species ArialDetachedLabel&Ctl23_Species0 x9 d5U678"`Sbwce24 Season0 x9 24 Season ArialDetachedLabel$Ctl24_Season0 x9 d5]678"`cbce$26 Abundance0 x9 26 Abundance ArialDetachedLabel*Ctl26_Abundance0 x9 d5W678"`sbsce"31 Criteria0 x9 31 Criteria ArialDetachedLabel(Ctl31_Criteria0 x9 d5U678"`Dbcce32 Notes0 x9 32 Notes ArialDetachedLabel"Ctl32_Notes0 x9 d5U68"`'bceLabel39Pop min Ariald5U68"`S+bc eLabel40max Ariald5U68"`/bc eLabel41accracy Ariald5U68"`4bc eLabel42Year Ariald5U68"`7bceLabel43Pop trend Ariald5U68"`s>bc eLabel44Trend acc Ariald5U678"` brceLabel4623 English Name ArialDetachedLabel 5Byja ;``m7U:<"`aZbe 23 Species23 Species ArialCtl23_Speciesm 27U:<"`DaZbw cve k32 Notes32 Notes ArialCtl32_Noteso05U8:"`b cdZef nOther significant assemblage of waterbird speciesRegionally significant species such as Woolly-necked Stork (12 birRegionally significant species such as Woolly-necked Stork (12 birds recorded in 2002) and Asian Openbill (27 birds recorded in 2002).Other significant assemblage of waterbird species are 2000 Pond Heron species, 600 Intermediate Egrets, 230 Pheasant-tailed Jacanas and 85 Black-winged Stilts. Many shorebird species also occur in the area such as Black-taile Godwit, Marsh Sandpiper, Wood Sandpiper, Common Sandpiper, Common Greenshank, Asiatic Golden Plover, Little Ringed Plover, Kentish Plover etc.The site also supports many shorebird species such as Asiatic Golden Plover, Little-ringed Plover, Kentish Plover, Greater sand Plover, Bar-tailed Godwit, Common Greenshank, Green Sandpiper, Wood Sandpiper, Common Sandpiper, Curlew Sandpiper.Other regionally significant species were also recorded from the the site such as Asian Openbill, Glossy Ibis, River Tern, Baya Weaver, Collared Kingfisher and Grey-headed Lapwing.on 29 September 2002 74 Asian Openbills were recorded.8 Lesser Frigatebirds, 1 Bridled Tern and 1 Peregrine Falcon were recorded on 23 February 1999.Other regionally significant species occur at the site such as Grey Heron, Great Egret, Little Cormorant, Brahminy Kite and Asian Openbill.Other regionally significant species present: Grey Heron, Brahminy Kite, River Lapwing, Red-wattled Lapwing, Small Pratincole, Great Thick Knee, River Tern, Pied Kingfisher, Baya Weaver.The site holds the Globally threatened species such as Sarus Crane (Grus antigone), Milky Stork (Mycteria cinerea), Painted Stork (Myctetria leucocephala) and Lesser Adjutant (Leptoptilos javanicus). During the survey on 29-30 May 2002, 23 Woolly-necked Storks were observed feeding where Prang villagers reported to have Sarus Cranes from 4-10 birds coming every year to feed in cultivated area (UTM: 0357181-1229107) located in the northeast of Prang village about 500m. Sarus Cranes reportedly present in this area from February to early May.RLVAL & '  ltural_intensificationx37-38P Agricultural intensificationxj Ctl37_38P_Aquaculture___fisheries37-38P Aquaculture / fisheriesd Ctl37_38P_Aquaculture___fisheriesx37-38P Aquaculture / fisheriesxj Ctl37_38P_Competition_from_introduced_animal_species37-38P Competition from introduced animal speciesd Ctl37_38P_Competition_from_introduced_animal_speciesx37-38P Competition from introduced animal speciesxj Ctl37_38P_Construction_of_dykes__dams37-38P Construction of dykes /damsd Ctl37_38P_Construction_of_dykes__damsx37-38P Construction of dykes /damsWith the exception of Koh Rong, the islands are mainly uninhabited, apart from a small military base on Koh Rong Samlem. Threats to biodiversity at the IBA include human disturbance, especially from fishinWith the exception of Koh Rong, the islands are mainly uninhabited, apart from a small military base on Koh Rong Samlem. Threats to biodiversity at the IBA include human disturbance, especially from fishing activities, and, potentially egg and chick collection by local people. Tourism development, particularly on Koh Pos, is a potential future threat, as it could disturb breeding beaches for Malaysian Plover.Although the IBA is uninhabited, apart from a small military base, the major threats to biodiversity are disturbance from human activities, especially fishing, and, potentially, hunting and egg and chick collection by resident military personnel and visiting fishermen. Another potential threat is introduction of alien predators, such as cats and dogs, to the islands, which could threaten the largely terrestrial Nicobar Pigeon.Within the IBA, hunting pressure on bird populations appears to be relatively low, and largely restricted to the snaring of ground birds, such as Chestnut-headed Partridge, Silver Pheasant Lophura nycthemera and Coral-billed Ground Cuckoo Carpococcyx renauldi, for domestic consumption. Such snaring is mainly conducted by agarwood collectors. Another potential threat to biodiversity is selective logging, which can lead to habitat degradation and loss. This threat is, however, currently low, since no large-scale, commercial logging is taking place within the IBA, and small-scale, illegal logging is on the decline.One of the major threats to biodiversity at the IBA is hunting, which is a particular threat to Bengal Florican. While hunting pressure on this species at the IBA may not be as severe as in the breeding areas, the level and impact of hunting are not yet fully understood. Another threat is disturbance caused by local people cultivating wet-season rice in the IBA but this is not thought to be great. Finally, agricultural expansion is a potential future threat to both forest and wetland habitats at the IBA.During the dry season, as the waters of the Tonle Sap recede, large numbers of people move into the IBA from a radius of well over 50 km to fish, collect firewood and graze cattle. These activities cause considerable disturbance to waterbirds and nesting Bengal Floricans. In addition, opportunistic hunting and collection of eggs and chicks represent additional threats.The major on-going threat to biodiversity at the IBA is hunting, which is a particular threat to populations of hornbills, parakeets, green pigeons and Green Peafowl Pavo muticus. Hunting is also an indirect threat to vulture populations, as it threatens the populations of large ungulates, which represent their main source of food. Along the Srepok River, cutting of trees and clearance of land for agriculture occurs along the banks, and destructive fishing methods, particularly the use of poison and explosives, is also of concern. These represent threats to Masked Finfoot and other riverine bird species.LVAL _ pcuracyValue ListP"Reliable";"Incomplete";"Poor";"Unknown"1440 ArialTrend_accuracyo5U8:"c dZeYn "";"";"10";"100" 5Byja ;23 English Name23 English NameTable/Query(SELECT [Species Table].[23 English Name] FROM [Species Table] GROUP BY [Species Table].[23 EThere are many villages located close to the IBA, and the activities of local people, in particular fishing, are a sourceThere are many villages located close to the IBA, and the activities oThere are many villages located close to the IBA, and the activities of local people generate a high level of disturbance to bird populations.There are many villages located close to the IBA, and the activities of local people, in particular fishing, are a source of disturbance to bird populations. Hunting is also a problem. For example, a mixed colony of Darters and flying-foxes Pteropus sp., discovered in 2000, was reported disturbed by local people collecting eggs and hunting in the following year. A further problem is invasion by the alien plant species Mimosa pigra, which is taking over large areas of the marshes, to the detriment of the natural vegetation.The major threat to biodiversity at the IBA is collection of eggs and chicks. In recent years, local people have collected eggs and chicks of all species at all stages of development. This problem has been compounded by a lack of conservation activities at the IBA.Although grazing of livestock, small-scale extraction of timber, clearance of forest for cultivation, and general human activity take place at low levels within the IBA, it is notable that many of the field records of White-shouldered Ibis have come from areas with moderate to high levels of disturbance. Perhaps a greater potential threat to the population of White-shouldered Ibis is over-exploitation, for example, in 1999, two juveniles were opportunistically collected from nest in the IBA. One obstacle to the conservation of this species is a lack of understanding of its ecology and the reasons for its dramatic decline in other parts of its range. The biggest potential threat to biodiversity at the IBA is posed by plans to grant a land concession in western Siem Pang District for the establishment of a plantation, which would likely have irreversible impacts on the habitat of White-shouldered Ibis and other globally threatened and near-threatened bird species.Hunting is currently the most serious threat to Bengal Florican and waterbirds at the IBA.. During the dry season, as floodwaters recede, large numbers of people move into the area to fish, harvest grasses, gather brushwood and wetland plants, and graze domestic livestock in herds that can number several hundred animals. This causes high levels of disturbance in some parts of the IBA. Deepwater rice is cultivated rather patchily in northern parts of the IBA. A potential future threat to biodiversity at the IBA is conversion of grassland areas to deepwater rice cultivation.The biodiversity of the IBA is under severe and immediate threat. Local people report that, each year, poison is used to hunt Sarus Cranes for food. However, the most serious threat is habitat loss. In recent years, a large proportion of the natural habitat at the IBA has been converted into agricultural land and aquacultural ponds. Drainage canals have already been dug into the most significant remaining areas of seasonally inundated grassland, and it is very likely that, without immediate and effective conservation action, all remaining areas of natural habitat at the IBA will soon be lost.LVAL2One Glossy Ibis was recorded in 1998 feeding on the mouth of Sekong River close to Koh Dat. Some other regionally significant species were also recorded during the survey conducted in May 2002 such as Great Thick-knee (Esacus recurvirostris), Small Pratincole (Glareola lactea), River Lapwing (Vanellus duvaucelii), River Tern (Sterna aurantia) and Woolly-necked Stork (Ciconia episcopus). During the survey, a total of 10 Great Thick-knees (Esacus recurvirostris) were seen along the Sekong river, between Stung Treng town (UTM 0604662 1496202) and a point 3 km downstream of the Laotian border (UTM 0644578 1593125). On 22 May 2002, a total of 21 River Lapwings (Vanellus duvaucelii) were seen along the Sekong river, between Stung Treng town and a point 3 km downstream of the Laotian border. On 24 May 2002, a total of 14 birds were seen along the Sekong river between Siem Pang town and Stung Treng town. Taking the higher of the two counts for the stretch between Siem Pang and Stung Treng towns, the minimum count of River Lapwing along the Cambodian part of the Sekong river is 35 birds. This compares with a count of c.211 birds along a 200 km stretch of the Se San river, during May 1998 (Timmins and Men Soriyun 1998). The difference in number of birds recorded can be attributed to the fact that, during the survey along the Se San river, exposed sandbars were present along greater than 60% of the total river length, whereas, during the survey along the Sekong river, exposed sandbars were present along less than 15% of the total river length. On 19 May 2002, a total of 16 Small Pratincoles (Glareola lactea) were seen along the Sekong river between Stung Treng town and Siem Pang town. On 22 May 2002, a total of 20 birds were seen along the Sekong river, between Stung Treng town and a point 3 km downstream of the Laotian border. On 24 May 2002, a total of 16 birds were seen along the Sekong river between Siem Pang town and Stung Treng town. On 19 May 2002, a total of 31 River Terns (Sterna aurantia) were seen al LVAL b c*37-38P Intensified forest managementxIntensified forest managementArial-Ctl37_38P_Intensified_forest_managementxj2]`abi#*37-38P Introduction of exotic plan species*37-38P Introduction of exotic plan species-Ctl37_38P_Introduction_of_exotic_plan_speciesd5]68"`<ab c037-38P Introduction of exotic plan speciesx#Introduction of exotic plan speciesArial3Ctl37_38P_Introduction_of_exotic_plan_speciesxj2_`abi%37-38P Natural events37-38P Natural eventsCtl37_38P_Natural_eventsd5_68"`<abc37-38P Natural eventsxNatural eventsArialCtl37_38P_Natural_eventsxj2`abi'37-38P Recreation, tourism37-38P Recreation, tourismCtl37_38P_Recreation__tourismd5_68"`<abc 37-38P Recreation, tourismxRecreation, tourismArial#Ctl37_38P_Recreation__tourismxj2`abi)"37-38P Selective logging / cutting"37-38P Selective logging / cutting%Ctl37_38P_Selective_logging___cuttingd5_68"`<ab~ c(37-38P Selective logging / cuttingxSelective logging / cuttingArial+Ctl37_38P_Selective_logging___cuttingxj2`acbi+37-38P Undergrazing37-38P UndergrazingCtl37_38P_Undergrazingd568"`<acb$c37-38P Undergrazingx UndergrazingArialCtl37_38P_Undergrazingxj2`abbi-!37-38P Unsustainable exploitation!37-38P Unsustainable exploitation$Ctl37_38P_Unsustainable_exploitationd5]68"`<abbQ c'37-38P Unsustainable exploitationxUnsustainable exploitationArial*Ctl37_38P_Unsustainable_exploitationxj2`aCbi/ 37-38P Other 37-38P OtherCtl37_38P_Otherd5_68"`<aRbc37-38P OtherxOtherArialCtl37_38P_Otherxj2U`aQbi137-38P Unknown37-38P UnknownCtl37_38P_Unknownd5W68"`<aBbc37-38P UnknownxUnknownArialCtl37_38P_Unknownxd5U68`IaKb ce x102TypeCenturyd5U68`] aibce x103 37 PresenceCenturyd5U68`gaZbce x104 38 ImportanceCenturyo5]8:"`b@ cdehn"";"";"";"";"10";"2"137-38I Abandonment / reduction of land management137-38I Abandonment / reduction of land management Table/Query Threat LevelArial4Ctl37_38I_Abandonment___reduction_of_land_managemento5]8:"`b@ cdehn"";"";"";"";"10";"2"#37-38I Agricultural intensification#37-38I Agricultural intensification Table/Query Threat LevelArial&Ctl37_38I_Agricultural_intensificationo5W8:"`b@ cdehn"";"";"";"";"10";"2"37-38I Afforestation37-38I Afforestation Table/Query Threat LevelArialCtl37_38I_Afforestationo5_8:"`b@ cdehn"";"";"";"";ong the Sekong river between Stung Treng town and Siem Pang town (UTM 0650208 1560485). On 22 May 2002, a total of 11 birds were seen along the Sekong river, between Stung Treng town and a point 3 km downstream of the Laotian border. On 24 May 2002, a total of 20 birds were seen along the Sekong river between Siem Pang town and Stung Treng town. On 19 May 2002, two Woolly-necked Storks (Ciconia episcopuswere) seen in flight above gallery forest along the western bank of the Sekong river (UTM 0635490 1527343). On 20 May 2002, two birds were seen feeding at a seasonal wetland, about 1 ha in area, called Trapaeng Prolit Touch (UTM 0644374 1566530).LVAL%  wb__tH[wb_[ڍmIDjCtl37_38P_Abandonment___reduction_of_land_management37-38P Abandonment / reduction of land managementd Ctl37_38P_Abandonment___reduction_of_land_managementx37-38P Abandonment / reduction of land managementxjCtl37_38P_Afforestation37-38P Afforestationd Ctl37_38P_Afforestationx37-38P AfforestationxjCtl37_38P_Agricultural_intensification37-38P Agricultural intensificationd Ctl37_38P_Agricultural_intensificationx37-38P Agricultural intensificationxj Ctl37_38P_Aquaculture___fisheries37-38P Aquaculture / fisheriesd Ctl37_38P_Aquaculture___fisheriesx37-38P Aquaculture / fisheriesxj Ctl37_38P_Competition_from_introduced_animal_species37-38P Competition from introduced animal speciesd Ctl37_38P_Competition_from_introduced_animal_speciesx37-38P Competition from introduced animal speciesxj Ctl37_38P_Construction_of_dykes__dams37-38P Construction of dykes /damsd Ctl37_38P_Construction_of_dykes__damsx37-38P Construction of dykes /damsxjCtl37_38P_Deforestation__commercial_37-38P Deforestation (commercial)d Ctl37_38P_Deforestation__commercial_x37-38P Deforestation (commercial)xjCtl37_38P_Disturbance_to_birds37-38P Disturbance to birdsd Ctl37_38P_Disturbance_to_birdsx37-38P Disturbance to birdsxjCtl37_38P_Drainage37-38P Drainaged Ctl37_38P_Drainagex37-38P DrainagexjCtl37_38P_Dredging_and_canalization37-38P Dredging and canalizThreats to biodiversity at the IBA have yet to be evaluated in detail. However, one of the major threats is thought to be opportunistic hunting of birdThreats to biodiversity at the IBA have yet to be evaluated in detail. However, one of the major threats is thought to be opportunistic hunting of birds by local people fishing with spotlights at night, during the wet season. Bengal Floricans were at least formerly targeted by some hunters in this IBA.The construction of new roads and logging roads is facilitating access to the area for returning refugees and, particularly in the lowland areas, forest is being converted to agriculture. Hunting, often linked with new roads and increasing access is also a problem. Much of it is for local consumption, and linked with the collection of kresna (Aquilaria malaccensis), but hunting for trade, particularly from Thailand is thought to be increasing.The inhabitants Prasat Tuyo fishing village depend on the natural resources of the IBA, and their activities are potentially a source of disturbance to waterbird populations. A more serious threat to biodiversity at the IBA is hunting of waterbirds, particularly the use of poison.Opportunistic hunting of waterbirds is probably the most serious threat to biodiversity at the IBA. Several small, mobile, floating villages are dotted throughout the area, including Kampong Loung, Chhnuk Tru and Phat Sanday, and fishing activities are a source of disturbance to bird populations.Cutting of trees and clearance of land for agriculture occurs along both banks of the Sekong River, particularly along the lower sections and around Siem Pang town. During the dry season, the temporary fishing camps that are established at sections of channel mosaic habitat are a particular cause for concern, as they represent a source of disturbance to sandbar breeding birds. This disturbance can take the form of direct persecution, through hunting or egg collection, or accidental disturbance to nesting birds. A potential future threat to the IBA is the development of hydropower schemes upstream along the Sekong River or its tributaries, which may lead to changs in flow patterns with negative impacts on riverine birds. " @ @ @ @ @'''''''' ' '  ' ' ' ' '''''''''''''' '!'"'#'$' %'!&'")'#+'$,'%-'&.''YYIdParentIdName         Arial>Ctl13_Central_Coordinates_Lon_2m57U`habpi k 14 Altitude Min14 Altitude IBA CodemCtl5_Final_IBA_Code5 Final IBA CodemCtl6_National_Site_Name6 National Site NamemCtl7_International_Site_Name7 International Site Namem Ctl8_Country8 Countrym Ctl9_Administrative_Region__Level_1_9 Administrative Region (Level 1)m Ctl10_Administrative_Region__Level_2_10 Administrative Region (Level 2)m Ctl11_Area11 Aream Ctl12_Area_Accuracy12 Area AccuracymCtl13_Central_Coordinates_Lat_113 Central Coordinates Lat 1mCtl13_Central_Coordinates_Lat_213 Central Coordinates Lat 2mCtl13_Central_Coordinates_Lat_313 Central Coordinates Lat 3mCtl13_Central_Coordinates_Lon_113 Central Coordinates Lon 1mCtl13_Central_Coordinates_Lon_213 Central Coordinates Lon 2mCtl13_Central_Coordinates_Lon_313 Central Coordinates Lon 3mCtl14_Altitude_Min14 Altitude MinmCtl14_Altitude_Max14 Altitude MaxjCtl16_Management_Plan16 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Map_Labeld+Ctl16_Management_Plan_Label16 Management Plan_Labeld,Ctl17_Ownership_Label17 Ownership_Labeld-Ctl18_General_Description_Label18 General Description_Labeld.Ctl19_EBA_Code_Proposed_Label19 EBA Code Proposed_Labeld/Ctl20_Biome_Code_Proposed_Label20 Biome Code Proposed_Labeld0Ctl21_Criteria_Proposed_Label21 Criteria Proposed_Labeld1Ctl22_Criteria_Notes_Label22 Criteria Notes_Labelp2Habitat_TableHabitat Tablep3Species_Table_subreportSpecies Table subreportp4Landuse_Table_subreportLanduse Table subreportp5Threats_Table_subreportThreats Table subreportp6Additional_Info_Table_subreportAdditional Info Table subreportd7Label285d8B " @ @ @ @ @'''''''' ' '  ' ' ' ' '''''''''''''' '!'"'#'$' %'!&'")'#+'$,'%-'&.''bitat Table Form.Form.Habitat Table FormIDSerial number"[Event Procedure]$Habitat_Table_Formd5U8`a*bcd e0Habitat Table Form0 x9 (HABITATS AND % COVERCentury0Habitat_Table_Form0 x9 p3W`a4b4&c6d$Landuse Table Form.Form.Landuse Table FormIDSerial number$Landuse_Table_Formd5]8`aM3b c,d e0Landuse Table Form0 x9 &LANDUSE AND % COVERCentury"[Event Procedure]0Landuse_Table_Form0 x9 p3W`aCtl13_Central_Coordinates_Lat_3o05Ucdef,l n813 Central Coordinates Lon 3813 Central Coordinates Lat 3Value List"N";"S" Arial>Ctl13_Central_Coordinates_Lon_3p3U`ajSbq%cd4Additional Info Table Form>Form.Additional Info Table FormIDSerial number4Additional_Info_Table_Formd5]8`a7Rbcd e@Additional Info Table Form0 x9 ,ADDITIONAL INFORMATIONCentury@Additional_Info_Table_Form0 x9 d5U`aZbc;d eX0 x9 173Delete Record Arialo05W`b@ cr$defl nR {17517 OwnershipValue List"P";"Private";"S";"State";"C";"Commercial";"R";"Religious";"I";"International waters";"O";"Other";"U";"Unknown"1440;1440 ArialR _175d5]`T$a bHcd $17 Ownership 17 Ownership Arial*Ctl17_Ownership d5]8`aBb c;d e0 x9 177PROTECTED AREASCenturyd5U8`Jab6cd e0 x9 178CRITERIACenturyd5]8`aJbc,d e0 x9 179LLOBBYING / CAMPAIGNING FOR LEGISLATIONCenturyo05U`b@ c!de:l nR {182 12 Area AccuracyValue List|"A";"10% Error";"B";xYYtz}N77 Y  Y dBiome CodeBiome Nameonment___reduction_of_land_management37-38I Abandonment / reduction of land managemento9Ctl37_38I_Agricultural_intensification37-38I Agricultural intensificationo:Ctl37_38I_Afforestation37-38I Afforestationo;Ctl37_38I_Aquaculture___fisheries37-38I Aquaculture / fisherieso<Ctl37_38I_Competition_from_introduced_animal_species37-38I Competition from introduced animal specieso=Ctl37_38I_Construction_of_dykes__dams37-38I Construction of dykes /damso>Ctl37_38I_Deforestation__commercial_37-38I Deforestation (commercial)o?Ctl37_38I_Disturbance_to_birds37-38I Disturbance to birdso@Ctl37_38I_Drainage37-38I DrainageoACtl37_38I_Dredging_and_canalization37-38I Dredging and canalizationoBCtl37_38I_Extraction_industry__mining_37-38I Extraction industry (mining)oCCtl37_38I_Firewood_collection37-38I Firewood collectionoDCtl37_38I_Forest_grazing37-38I Forest grazingoECtl37_38I_Groundwater_abstraction37-38I Groundwater abstractionoFCtl37_38I_Industrial___urban_development37-38I Industrial / 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Print_Report_A_to_BPrint Report A to Bstry (mining)hhhhxj2_`a! bPropData35TypeInfo6BlobDelta0109΍ yBlob hPropData8:TypeInfo;M#BlobDelta08=Babc +e ghi j.k5[IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary$dv1 @ @ @ @ IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code], [IBA Data Form].[4 Temporary IBA Code](rV>@IBA Data Form Arial8,{ 6{K q: u I  77 Y  Y dBiome CodeBiome Namedary Ariald5U`\abcd Label77 15 Map Arialo5Ucd6 e l n%"";"";"10";"60"8 Country8 CountryTable/QuerySELECT [Country Table].[Country Name] FROM [Country Table] ORDER BY [Country Table].[Country Name]; ArialCtl8_Countryd5U`a bcd 8 Country0 x9 8 Country Arial$Ctl8_Country0 x9 h1U`,ab@c@i&Delete RecordCommand0"[Event Procedure]D( Ȥ 6Ӿ,u@Ӿ,u@Biome Table66666666666 "ڕ,u@Ӿ,u@Additional Info TableJJJJJJJJJJJ ڕ,u@ڕ,u@~sq_rThreats Table subreportXXXXXXXXXXX ڕ,u@ڕ,u@~sq_rSpecies Table subreportXXXXXXXXXXX ڕ,u@ڕ,u@~sq_rSpecies TableDDDDDDDDDDD W,u@ڕ,u@~sq_rR threats<<<<<<<<<<< W,u@W,u@~sq_rR SpeciesAreaCompilerTTTTTTTTTTT W,u@W,u@~sq_rR Species NoteFFFFFFFFFFF W,u@W,u@~sq_rR Species at IAB SitesVVVVVVVVVVV ,u@,u@~sq_rR Site decriptionLLLLLLLLLLL ,u@,u@~sq_rR Site AccountFFFFFFFFFFF ,u@,u@~sq_rR Secondary SpeciesPPPPPPPPPPP ,u@,u@~sq_rR ReferencesBBBBBBBBBBB ,u@,u@~sq_rR IBA Site AccountNNNNNNNNNNN ,u@,u@~sq_rProtected Area Table subBiome15Sundaic Montane Forest# Biome14Sundaic Lowland Forest# Biome13Saharo-Sindian Desert" Biome12Indo-Gangetic Plains! Biome11Indo-Malayan Tropical Dry Zone+ Biome10Indian Peninsula Tropical Moist Forest3 Biome09Indochinese Tropical Moist Forest. Biome08Sino-Himalayan Subtropical Forest. Biome07Sino-Himalayan Temperate Forest, Biome06Irano-Turanian Mountains% Biome05Eurasian High Montane (Alpine and Tibetan)7 Biome04Eurasian Steppe and Desert' Biome03North-East Asian Temperate Forest. Biome02Boreal Forest (Taiga)" Biome01Arctic Tundra Y N:: Y  Y t(<Country CodeCountry Name(:<YCountry Codeuse Table Form0 x9 &LANDUSE AND % COVERCentury"[Event Procedure]0Landuse_Table_Form0 x9 p3W`aCtl13_Central_Coordinates_Lat_3o05Ucdef,l n813 Central Coordinates Lon 3813 Central Coordinates Lat 3Value List"N";"S" Arial>Ctl13_Central_Coordinates_Lon_3p3U`ajSbq%cd4Additional Info Table Form>Form.Additional Info Table FormIDSerial number4Additional_Info_Table_Formd5]8`a7Rbcd e@Additional Info Table Form0 x9 ,ADDITIONAL INFORMATIONCentury@Additional_Info_Table_Form0 x9 d5U`aZbc;d eX0 x9 173Delete Record Arialo05W`b@ cr$defl nR {17517 OwnershipValue List"P";"Private";"S";"State";"C";"Commercial";"R";"Religious";"I";"International waters";"O";"Other";"U";"Unknown"1440;1440 ArialR _175d5]`T$a bHcd $17 Ownership 17 Ownership Arial*Ctl17_Ownership d5]8`aBb c;d e0 x9 177PROTECTED AREASCenturyd5U8`Jab6cd e0 x9 178CRITERIACenturyd5]8`aJbc,d e0 x9 179LLOBBYING / CAMPAIGNING FOR LEGISLATIONCenturyo05U`b@ c!de:l nR {182 12 Area AccuracyValue List|"A";"10% Error";"B";"50% Error";"C";">50% Error";"U";"Unknown"1440;1440 ArialR _182d5U`!abcd R {182 12 Area accuracy ArialR _182 d5U`$abwcd 0 x9 184(ha) Arialh1]``'a$bHcIg hiCommand195SpeciesSearchOpen WBS Form Arialo05U`bc0 d el n List3.21 Criteria Proposed A4Value Listx"A4i";">=1% biogiographic population (Waterbirds)";"A4ii";">=1% global population (non waterbirds)";"A4iii";">=20,000 waterbirds or >=10,000 pairs of seabirds";"A4iv";"MigratoryBottleneck"1440;3885 Ariald5U`ab` cd D21 Criteria Proposed for IBA_Label821 Criteria Proposed for IBA Arial(v1 @ @ @ @ @JCtl21_Criteria_Proposed_for_IBA_Labelo5U`bcdefn*"";"";"";"";"10";"12" Combo5(19 EBA Code ProposedTable/QueryߪSELECT [EBA/SA Table].[EBA/SA Code], [EBA/SA Table].[EBA/SA Name] FROM [EBA/SA Table]1440;2850d5U`<abcd 419 EBA Code Proposed_Label(19 EBA Code Proposed Arial:Ctl19_EBA_Code_Proposed_Labelo5U`bcd!efn*"";"";"";"";"10";"14" Combo7,20 Biome Code ProposedTable/QueryߠSELECT [Biome Table].[Biome Code], [Biome Table].[Biome Name] FROM [Biome Table]1440;3914d5U`<ag b cd H20 Biome Code for Proposed IBA_Label<20 Biome Code for Proposed IBA ArialNCtl20_Biome_Code_for_Proposed_IBA_Labelo5WbwcdGen"";"";"10";"4"Combo204 Country CodeTable/QuerySELECT [Country Table].[Country Code] FROM [Country Table] ORDER BY [Country Table].[Country Code];375o5WbwcdGen "";"";"10";"4"Combo574 Country CodeTable/QuerySELECT [Country Table].[Country Code] FROM [Country Table] ORDER BY [Country Table].[Country Code];375o05U`bc0 d;el n!Combo60.21 Criteria Proposed A1Value ListD"A1";"Grobally Threatened Species"1440;1440 Ariald5U` a;bwcd Label62[A1] Ariald5U` a bwcd Label63[A4] Arialp3U`a'\b%cGd"0Key Reference Table Form:Form.Key Reference Table FormIDSerial number0Key_Reference_Table_Formd5U`a[bcd e>gg Y  Y t(xEBA/SA CodeEBA/SA Name>A<YEBA/SA Coden forest33-34C Hill evergreen forest Ctl33_34C__Hill_evergreen_forestS5Q).nj`a\ i33-34P Pine forest33-34P Pine forestCtl33_34P_Pine_forestS5Q).nd78`a/ bucd e33-34P Pine forest_Label Pine forestTimes New RomanCtl33_34P_Pine_forest_LabelS5Q).nm5<"C`<a\ bck33-34C Pine forest33-34C Pine forestCtl33_34C_Pine_forestS5Q).nj`ai)33-34P Montane broadleaf evergreen forest)33-34P Montane broadleaf evergreen forest,Ctl33_34P_Montane_broadleaf_evergreen_forestS5Q).nd78`a.b cd e/33-34P Montane broadleaf evergreen forest_Label"Montane broadleaf evergreen forestTimes New Roman2Ctl33_34P_Montane_broadleaf_evergreen_forest_LabelS5Q).nm5<"C`<abck)33-34C Montane broadleaf evergreen forest)33-34C Montane broadleaf evergreen forest,Ctl33_34C_Montane_broadleaf_evergreen_forestS5Q).nj`ai)33-34P Montane broadleaf deciduous forest)33-34P Montane broadleaf deciduous forest,Ctl33_34P_Montane_broadleaf_deciduous_forestS5Q).nd78`a<b cd e/33-34P Montane broadleaf deciduous forest_Label"Montane broadleaf deciduous forestTimes New Roman2Ctl33_34P_Montane_broadleaf_deciduous_forest_LabelS5Q).nm5<"C`<axbck)33-34C Montane broadleaf deciduous forest)33-34C Montane broadleaf deciduous forest,Ctl33_34C_Montane_broadleaf_deciduous_forestS5Q).nj`ai033-34P Montane mixrd broadleaf-coniferous forest033-34P Montane mixrd broadleaf-coniferous forest3Ctl33_34P_Montane_mixrd_broadleaf_coniferous_forestS5Q).nd78`a;b cd e633-34P Montane mixrd broadleaf-coniferous forest_Label)Montane mixrd broadleaf-coniferous forestTimes New Roman9Ctl33_34P_Montane_mixrd_broadleaf_coniferous_forest_LabelS5Q).nm5<"C`<abck033-34C Montane mixrd broadleaf-coniferous forest033-34C Montane mixrd broadleaf-coniferous forest3Ctl33_34C_Montane_mixrd_broadleaf_coniferous_forestS5Q).nj`ai 33-34P Montane coniferous forest 33-34P Montane coniferous forest#Ctl33_34P_Montane_coniferous_forestS5Q).nd78`aIbCcd e&33-34P Montane coniferous forest_LabelMontane coniferous forestTimes New Roman)Ctl33_34P_Montane_coniferous_forest_LabelS5Q).nm5<"C`<abck! 33-34C Montane coniferous forest 33-34C Montane coniferous forest#Ctl33_34C_Montane_coniferous_forestS5Q).nj`ai"!33-34P Broadleaf deciduous forest!33-34P Broadleaf deciduous forest$Ctl33_34P_Broadleaf_deciduous_forestT5Q).nd78`aWb4cd e'33-34P Broadleaf deciduous forest_LabelBroadleaf deciduous forestTimes New Roman*Ctl33_34P_Broadleaf_deciduous_forest_LabelT5Q).nm5<"C`<abck#!33-34C Broadleaf deciduous forest!33-34C Broadleaf deciduous forest$Ctl33_34C_Broadleaf_deciduous_forestT5Q).nj`ai$(33-34P Mixed broadleaf-coniferous forest(33-34P Mixed broadleaf-coniferous forest+Ctl33_34P_Mixed_broadleaf_coniferous_forestT5Q).nd78aVb_ cd e.33-34P Mixed broadleaf-coniferous forest_Label!Mixed broadleaf-coniferous forestTimes New Roman1Ctl33_34P_Mixed_broadleaf_coniferous_forest_LabelT5Q).nm5<"C`<abck%(33-34C Mixed broadleaf-coniferous forest(33-34C Mixed broadleaf-coniferous forest+Ctl33_34C_Mixed_broadleaf_coniferous_forestT5Q).nj`ai&33-34P Coniferous forest33-34P Coniferous forestCtl33_34P_Coniferous_forestT5Q).nd78adbdcd e33-34P Coniferous forest_LabelConiferous forestTimes New Roman!Ctl33_34P_Coniferous_forest_Label0v1Site Namexm Ctl9_Administrative_Region__Level_1_9 Administrative Region (Level 1)d Ctl9_Administrative_Region__Level_1_x9 Administrative Region (Level 1)xmCtl10_Administrative_Region__Level_2_10 Administrative Region (Level 2)d Ctl10_Administrative_Region__Level_2_x10 Administrative Region (Level 2)xmCtl11_Area11 Aread Ctl11_Areax11 AreaxmCtl13_Central_Coordinates_Lat_113 Central Coordinates Lat 1d Ctl13_Central_Coordinates_Lat_1x13 Central Coordinates Lat 1xmCtl13_Central_Coordinates_Lat_213 Central Coordinates Lat 2mCtl13_Central_Coordinates_Lon_113 Central Coordinates Lon 1d Ctl13_Central_Coordinates_Lon_1x13 Central Coordinates Lon 1xmCtl13_Central_Coordinates_Lon_213 Central Coordinates Lon 2mCtl14_Altitude_Min14 Altitude Mind Ctl14_Altitude_Minx14 Altitude MinxmCtl14_Altitude_Max14 Altitude Maxd >x135d ?x136m@Ctl18_General_Description18 General Descriptiond ACtl18_General_Descriptionx18 General DescriptionxmBCtl22_Criteria_Notes22 Criteria Notesd CCtl22_Criteria_Notesx22 Criteria NotesxpFSpecies_TableSpecies Tabled Gx137oHCtl16_Management_Plan16 Management Pland ICtl16_Management_Planx16 Management Planxd Jx154d Kx155pLHabitat_Table_FormHabitat Table Formd MHabitat_Table_FormxHabitat Table FormxpNLanduse_Table_FormLanduse Table Formd OLanduse_Table_FormxLanduse Table FormxpPThreats_Table_FormThreats Table Formd QThreats_Table_FormxThreats Table FormxoRCtl13_Central_Coordinates_Lat_313 Central Coordinates Lat 3oSCtl13_Central_Coordinates_Lon_313 Central Coordinates Lon 3pTAdditional_Info_Table_FormAdditional Info Table Formd UAdditional_Info_Table_FormxAdditional Info Table Formxd Vx173oWR_175R{175d XCtl17_Ownership17 Ownershipd Yx177d Zx178d [x179o`R_182R{182d aR_182R{182d bx184h gCommand195ojList3d kCtl21_Criteria_Proposed_for_IBA_Label21 Criteria Proposed for IBA_LabelolCombo5d mCtl19_EBA_Code_Proposed_Label19 EBA Code Proposed_LabelonCombo7d oCtl20_Biome_Code_for_Proposed_IBA_Label20 Biome Code for Proposed IBA_LabelouCombo20ovCombo57owCombo60d xLabel62d yLabel63pzKey_Reference_Table_FormKey Reference Table Formd {Key_Reference_Table_Form_LabelKey Reference Table Form Labelj|Check73d }Label74j~Check75d Label76d Label77oCtl8_Country8 Countryd Ctl8_Countryx8 Countryxh Delete_RecordDelete RecordSerial number4 Country Code12 Area Accuracy15 Map 1 Known Boundary15 Map 2 Digitized Boundary17 Ownership19 EBA Code Proposed20 Biome Code Proposed21 Criteria Proposed A121 Criteria Proposed A4pProtected_Area_Table_FormProtected Area Table FormpIntervention_Table_FormIntervention Table FormmText6d Label7mCtl66_Secondary_criteria_proposed_for_the_IBA66 Secondary criteria proposed for the IBAd Label8mCtl67_Globally_threatened_primate_species67 Globally threatened primate speciesd Label9mCtl68_Globally_threatened_turtle_and_crocodile_species68 Globally threatened turtle and crocodile speciesd Labe =fxR,wU0  ^ -  { U 4  q L 0 h = # i P 6  oEZ4 wN$a6 nMyH*e8yN#teneSA106Mentawai Islands SA105Simeulue SA104North Sumatran lowlands" SA103Riau and Lingga islands" SA102Malayan peninsula lowlands% SA101Natuna Islands SA100Bornean coastal zone SA99Kalimantan lowlandsSA98Sabah lowlandsSA97North-east Bornean islands$SA96SiquijorSA95Tablas, Romblon and Sibuyan%SA94Batanes and Babuan Islands$SA93LanyuSA92Japanese and Korean offshore islands.SA91Iwo IslandsSA90Central Honshu montane forests(SA89Central Honshu lowland forest'SA88SakhalinSA87Chukoski PeninsulaSA86Peninsular Thailand lowland forests-SA85Thailand-Cambodia mountains%SA84Kontum PlateauSA83Southern LaosSA82Fan-Si-Pan and northern Laos&SA81Doi Ching DaoSA80Myanmar-Thailand mountains$SA79Northern Myanmar lowlands#SA78Northern Qinghai-Tibetan"SA77Mongolian mountainsSA76Southern Xinjiang mountains%SA75Central Indian forests SA74Indus plainsSA73Afganistan mountainsSA72Southern Deccan Plateau!SA71Eastern Andhra Pradesh EBA188Christmas Island EBA187North-east Australia EBA186South-west Australia EBA185Tasmania EBA184South-east Australia EBA183Eastern Australia EBA182Queensland wet tropics" EBA181Cape York EBA180Trans-Fly EBA179South Papuan lowlands! EBA178Central Papuan mountains$ EBA177Adelbert and Huon ranges$ EBA176North Papuan lowlands! EBA175North Papuan mountains" EBA174Geelvink Islands EBA173West Papuan highlands! EBA172West Papuan lowlands EBA171Northern Maluku EBA170Seram EBA169Buru EBA168Banggai and Sula Island# EBA167Sangihe and Talaud EBA166Sulawesi EBA165Banda Sea Islands EBA164Timor and Wetar EBA163Sumba EBA162Northern Nusa Tenggara" EBA161Javan coastal zone EBA160Java and Bali forests! EBA159Enggano EBA158Sumatora and Peninsular Malaysia, EBA157Bornean mountains EBA156Palawan EBA155Sulu archipelago EBA154Mindoro and the Eastern Visayas+ EBA153Cebu EBA152Negros and Panay EBA151Luzon EBA150Mindoro EBA149Taiwan EBA148Nansei Shoto EBA147Ogasawara Islands EBA146Izu Islands EBA145Da Lat plateau EBA144South Vietnamese lowlands% EBA143Annamese lowlands EBA142Hainan EBA141South-east Chinese mountains( EBA140Chinese subtropical forest& EBA139Yunnan mountains EBA138West Sichuan mountains" EBA137Central Sichuan mountains% EBA136Shanxi mountains EBA135Qingai mountains EBA134Eastern Tibet EBA133Southern Tibet EBA132Irrawaddy plains EBA131Assam Plains EBA130Eastern Himalayas EBA129Central Himalayas EBA128Western Himalayas EBA127Taklimakan Desert EBA126Nicobar Islands EBA125Andaman Islands EBA124Sri Lanka EBA123Western Ghats =veatened elephant and ungulate speciesd Label12d Label13mCtl13_Central_Coordinates_Lat_413 Central Coordinates Lat 4mCtl13_Central_Coordinates_Lon_413 Central Coordinates Lon 4mCtl71_Recommendations71 RecommendationsTable].[EBA/SA Code], [EBA/SA Table].[EBA/SA Name] FROM [EBA/SA Table]1440;2850d5U`<abcd 419 EBA Code ProposedoooddpdjdjddodhppmdmdmdmdmdmdmdmmCombo7,20 Biome Code Propose08=Babce gh itjhk -@World Bird ListWorld Bird List Ariald2e12f5g237hghMS Sans Serifi1ghj1ghk1l23:m4117@>΍ ΍ Blob @PropData=?TypeInfon2o2p5r35zijMS Sans Serif{5` DetailZd}n).nd5U`ab/ cd e Label6rSearch for the species and click "Select Species" button. Arial%Zd}n).nh1U`a bcXhSelect SpeciesSelect Species"[Event Procedure] ArialSelect_SpeciesGqГ).no5Ubcdden "";"";"10";"100"4C).nSCIENTIFICTable/QueryxSELECT [World Bird List].[SCIENTIFIC] FROM [World Bird List]1440d5U`<abcLabel17Scientific Name4C).n_Reference_Table_Formͬ $Zd}n).nDetail FAMILY SPECIESd Label6h Select_SpeciesSelect Speciesd Label17oSCIENTIFICCOMMONStata)bci#Check73.15 Map 1 Kno8Additional Info Table Form(Habitat Table Form2Intervention Table Form$IUCN PA Category4Key Reference Table Form(Landuse Table Form6Protected Area Table Form(Species Table FormDirDataAPropDataCmdbars΍ ΍ Modules ΍ ΍ (Threats Table Form(Control Panel Form IBA Data Form "World Bird List  11CB0 10CB0 9CB0 8CB0 7CB0 6CB0 5CB0 4CB0 3CB0 2CB0SA107Seribu Islands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kJ866?_kJ868?`kJ86:?akJ86<?bkJ86>?ckJ86@?dkJ86B?ekJ86D@kJD8?BkJD:?CkJD<?DkJD>?EkJD@?FkJDB?GkJDD?HkJDF?IkJDH?JkJF6?KkJF8?LkJF:?MkJF<?NkJF>?OkJF@?PkJFB?QkJFD?RkJFF?SkJFH?TkJH6?UkJH8?VkJH:?WkJH<?XkJH>?YkJH@?ZkJHB?[kJHD?\kJHF?]kJHH?^_1EMK΍ p Blob esPropDataJL      !"#$%&'()*+,-./0123456789:;<=>?@ABEHIJKLMNOPQRSTUVWXYZ[\]^_`abcdefghijklmnqrstuvwxyz{|}~-1 Habitat/Land Use 63-2 Threats 64 Lobbying or campeigning for legislationord Sp3W`aDbted Area Table Form> |Y?? Y@@ YAA YBB YCC YDD YEE YFF YGG YHH YII YJJ YKK YLL YMM YNN YOO YPP YQQ YRR YSS YTT YUU YVV YWW YXX YYY YZZ Y[[ Y\\ Y]] Y^^ Y__ Y`` Yaa Ybb Ycc Ydd Yee Yff Ygg Yhh Yii Yjj Ykk Yll Ymm Ynn Yoo Ypp Yqq Yrr Yss Ytt Yuu Yvv Yww Yxx Yyy Yzz Y{{ Y|| Y}} Y~~ Y Y Y Y Y Y Y Y  Y Y Y Y Y Y IDH33-34P Lowland evergreen rain forestH33-34C Lowland evergreen rain forestB33-34P Semi-evergreen rain forestB33-34C Semi-evergreen rain forest033-34P Peat swamp forest033-34C Peat swamp forest&33-34P Heath forest&33-34C Heath forest:v1T5Q).nd78` aAbcd e33-34P Scree and boulders_LabelScree and bouldersTimes New Roman"Ctl33_34P_Scree_and_boulders_LabelT5Q).nm5<"C`aLbcky33-34C Scree and boulders33-34C Scree and bouldersCtl33_34C_Scree_and_bouldersT5Q).nj`KaOiz 33-34P Caves 33-34P CavesCtl33_34P_CavesT5Q).nd78`a1b cd e33-34P Caves_LabelCavesTimes New RomanCtl33_34P_Caves_LabelT5Q).nm5<"C`aDbck{ 33-34C Caves 33-34C CavesCtl33_34C_CavesT5Q).nj`Ka?i|33-34P Arable land33-34P Arable landCtl33_34P_Arable_landT5Q).nd78` a0bcd e33-34P Arable land_Label Arable landTimes New RomanCtl33_34P_Arable_land_LabelT5Q).nm5<"C`a<bck}33-34C Arable land33-34C Arable landCtl33_34C_Arable_landT5Q).nj`Kaki~33-34P Rice paddies33-34P Rice paddiesCtl33_34P_Rice_paddiesT5Q).nd78` a/bcd e33-34P Rice paddies_Label Rice paddiesTimes New RomanCtl33_34P_Rice_paddies_LabelT5Q).nm5<"C`a4bck33-34C Rice paddies33-34C Rice paddiesCtl33_34C_Rice_paddiesT5Q).nj`Ka[i33-34P Improved pasture land33-34P Improved pasture landCtl33_34P_Improved_pasture_landT5Q).nd78` abcd e"33-34P Improved pasture land_LabelImproved pasture landTimes New Roman%Ctl33_34P_Improved_pasture_land_LabelT5Q).nm5<"C`a,bck33-34C Improved pasture land33-34C Improved pasture landCtl33_34C_Improved_pasture_landT5Q).nj`KaKi+33-34P Perennial crops, orchards and groves+33-34P Perennial crops, orchards and groves.Ctl33_34P_Perennial_crops__orchards_and_grovesT5Q).nd78` ab@ cd e133-34P Perennial crops, orchards and groves_Label$Perennial crops, orchards and grovesTimes New Roman4Ctl33_34P_Perennial_crops__orchards_and_groves_LabelT5Q).nm5<"C`a$bck+33-34C Perennial crops, orchards and groves+33-34C Perennial crops, orchards and groves.Ctl33_34C_Perennial_crops__orchards_and_grovesT5Q).nj`Ka;i/33-34P Forestry and agro-industrial plantations/33-34P Forestry and agro-industrial plantations2Ctl33_34P_Forestry_and_agro_industrial_plantationsT5Q).nd78` ab0 cd e533-34P Forestry and agro-industrial plantations_Label(Forestry and agro-industrial plantationsTimes New Roman8Ctl33_34P_Forestry_and_agro_industrial_plantations_LabelT5Q).nm5<"C`abck/33-34C Forestry and agro-industrial plantations/33-34C Forestry and agro-industrial plantations2Ctl33_34C_Forestry_and_agro_industrial_plantationsT5Q).nj`Ka+ i'33-34P Small settlements, rural gardens'33-34P Small settlements, rural gardens*Ctl33_34P_Small_settlements__rural_gardensT5Q).nd78` a b cd e-33-34P Small settlements, rural gardens_Label Small settlements, rural gardensTimes New Roman0Ctl33_34P_Small_settlements__rural_gardens_LabelT5Q).nm5<"C`a bck'33-34C Small settlements, rural gardens'33-34C Small settlements, rural gardens*Ctl33_34C_Small_settlements__rural_gardensT5Q).nj`Ka!i33-34P Urban areas33-34P Urban areasCtl33_34P_Urban_areasT5Q).nd78` a !bcd e33-34P Urban areas_Label Urban areasTimes New RomanCtl33_34P_Urban_areas_LabelT5Q).nm5<"C`a bck33-34C Urban areas33-34C Urban areasCtl33_34C_Urban_areas 0 LVAL@ 33-34C Sand dunes and beaches@33-34P Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone desert33-34P Oases33-34C Oases&33-34P Polar desert&33The IBA comprises the catchment of the upper Stung Sen river. The vegetation of the IBA is dominated by open deciduous dipterocarp forest (grading into mixed deciduous and semi-evergreen forest in the west), permanent and seasonal wetlands and grasslands.Much of the IBA is a floodplain and in the wet season, is inundated, while in the dry season, water is restricted to a few permanent watercourses (the Stung Sen river and its larger tributaries) and pools. Along these watercourses, semi-evergreen forest and thick bamboo forest are distributed. Much of the IBA is located within Kulen Promtep WildlifeThe IBA comprises the catchment of the upper Stung Sen river. The vegetation of the IBA is dominated by open deciduous dipterocarp forest (grading into mixed deciduous and semi-evergreen forest in the west), permanent and seasonal wetlands and grasslands.Much of the IBA is a floodplain and in the wet season, is inundated, while in the dry season, water is restricted to a few permanent watercourses (the Stung Sen river and its larger tributaries) and pools. Along these watercourses, semi-evergreen forest and thick bamboo forest are distributed. Much of the IBA is located within Kulen Promtep Wildlife Sanctuary. The IBA supports one of the few breeding colonies of Darter Anhinga melanogaster remaining outside of the Tonle Sap Lake floodplain. In addition, the IBA is an important breeding site for Sarus Crane Grus antigone and Lesser Adjutant Leptoptilos javanicus. Furthermore, a number of other globally threatened and near-threatened species have been recorded at the site, including Giant Ibis (Pseudibis gigantea), White-shouldered Ibis (Pseudibis davisoni), Greater Adjutant (Leptoptilos dubius), Black-necked Stork (Ephippiorhynchus asiaticus) and Grey-headed Fish Eagle (Ichthyophaga ichthyaetus). LVAL forest:33-34P Moist deciduous forest:33-34C Moist deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34The IBA comprises a large area of lowlands in south-western Mondulkiri and eastern Kratie provinces, which forms part of one of the largest remaining relatively undisturbed natural landscapes in mainland South-east Asia. The topography of the IBA is gently undulating, with elevations ranging from c.50 to 350 m asl. The vegetation of the IBA is characterised by a mosaic of semi-evergreen forest and deciduous dipterocarp forest, varying from open savanna to tall, closed canopy forest. Interspersed among these forest formations are pools, permanent streams and seasonally wet meadows, which are a major factor influencing the distriThe IBA comprises a large area of lowlands in south-western Mondulkiri and eastern Kratie provinces, which forms part of one of the largest remaining relatively undisturbed natural landscapes in mainland South-east Asia. The topography of the IBA is gently undulating, with elevations ranging from c.50 to 350 m asl. The vegetation of the IBA is characterised by a mosaic of semi-evergreen forest and deciduous dipterocarp forest, varying from open savanna to tall, closed canopy forest. Interspersed among these forest formations are pools, permanent streams and seasonally wet meadows, which are a major factor influencing the distribution of wildlife communities. The north-eastern part of the IBA is included within Phnom Prich Wildlife Sanctuary. The IBA supports one of the most intact remaining examples of the bird community of the dry forests of central Indochina, including such species as Giant Ibis Pseudibis gigantea, Green Peafowl Pavo muticus and Sarus Crane Grus antigone. Notably, the relative abundance of large ungulates means that the IBA may have greater potential to support viable populations of White-rumped, Long-billed and Red-headed Vultures Gyps bengalensis, G. indicus and Sarcogyps calvus than most other areas in mainland South-east Asia. LVAL and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone desert33-34P Oases33-34C Oases&33-34P Polar desert&33-34C Polar desertD33-34P Sea cliffs and rocky shoresD33-34C Sea cliffs and rocky shores<33-34P Rock stacks and islands<33-34C Rock stacks and islandsJ33-34P Inland cliffs and rocky slopesJ33-34C Inland cliffs and rocky slopes233-34P Scree and boulders233-34C Scree and boulders33-34P Caves33-34C Caves$33-34P Arable land$33-34C Arable land&33-34P Rice paddies&33-34C Rice paddies833-34P Improved pasture land833-34C Improved pasture landV33-34P Perennial crops, orchards and grovesV33-34C Perennial crops, orchards and groves^33-34P Forestry and agro-industrial plantations^33-34C Forestry and agro-industrial plantationsN33-34P- Steps should be taken to immediately protect the core area as conservation area similar to Ang Trapeang Thmor (IBA #1). - Enforcement activities should be initiated as soon as possibl- Enforcement activities should be initiated as soon as possibl- Enforcement activities should be initiated as soon as possible focusing on hunting of waterbirds and illegal fishing methods.- Steps should be taken to immediately protect the core area as conservation area similar to Ang Trapeang Thmor (IBA #1). - Enforcement activities should be initiated as soon as possible focusing on hunting of waterbirds and illegal fishing methods. - An education and awareness campaign should be undertaken in surrounding villages to gain local support for crane conservation - Any further irrigation or agricultural development in the area should not be undertaken without a full environmental impact assessment and a proper understanding of the potential effects on the natural wetland upon which the cranes are reliant. LVAL C Moist deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest The IBA comprises an area of seasonally inundated grassland in the floodplain of the Bassac River, which forms part of one of the largest areas of contiguous natural habitat remaining in the Mekong Delta. To the south and east, this area borders Vietnam, where the natural habitat has been almost entirely converted to agriculture. The IBA is inundated for 3 to 4 months each year, during which time a mat of floating vegetation, comprising around 30 aquatic plant species, forms. During the dryThe IBA comprises an area of seasonally inundated grassland in the floodplain of the Bassac River, which forms part of one of the largest areas of contiguous natural habitat remaining in the Mekong Delta. To the south and east, this area borders Vietnam, where the natural habitat has been almost entirely converted to agriculture. The IBA is inundated for 3 to 4 months each year, during which time a mat of floating vegetation, comprising around 30 aquatic plant species, forms. During the dry season, from December until May, the IBA supports a non-breeding population of Sarus Crane Grus antigone. After Ang Tropeang Thmor (KH001), this is the largest non-breeding population of this species known in Cambodia. The IBA also supports a number of other globally threatened and near-threatened bird species, most notably Bengal Florican Houbaropsis bengalensis. During 2002, the establishment of a Sarus Crane Conservation Area at the IBA was proposed by Department of Forestry and Wildlife. LVAL and beaches:33-34C Sand dunes and beaches@33-34P Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone desert33-34P Oases33-34C Oases&33-34P Polar desert&33-34C Polar desertD33-34P Sea cliffs and rocky shoresD33-34C Sea cliffs and rocky shores<33-34P Rock stacks and islands<33-34C Rock stacks and islandsJ33-34P Inland The IBA is located within Phnom Samkos Wildlife Sanctuary in the Cardamom Mountains, adjacent to the international border with Thailand. The IBA comprises all areas of evergreen and semi-evergreen forest above 400 m asl, which is thought to be the lower altitudinal limit of Chestnut-headed Partridge Arborophila cambodiana. The topography of the IBA is mountainous and dominated by three discrete peaks: Mount Samkos (1,717 m asl), Mount Khmaoch (1,496 m asl) and Mount Tumpor (c.1,250 m asl). At elevations up to 1,0The IBA is located within Phnom Samkos Wildlife Sanctuary in the Cardamom Mountains, adjacent to the international border with Thailand. The IBA comprises all areas of evergreen and semi-evergreen forest above 400 m asl, which is thought to be the lower altitudinal limit of Chestnut-headed Partridge Arborophila cambodiana. The topography of the IBA is mountainous and dominated by three discrete peaks: Mount Samkos (1,717 m asl), Mount Khmaoch (1,496 m asl) and Mount Tumpor (c.1,250 m asl). At elevations up to 1,000 m asl, the vegetation of the IBA is dominated by lowland evergreen forest, which has been disturbed by logging in many areas. At elevations between 1,000 and 1,300 m asl, lowland evergreen forest grades into hill evergreen forest. Above 1,300 m asl, near the summit of Mount Samkos, dwarf hill evergreen forest formations are found. The IBA supports both restricted-range species found in the Cambodia-Thailand-Mountains Endemic Bird Area: Chestnut-headed Partridge and Cambodian Laughingthrush (Garrulax ferrarius).Z | $k<ath forest:3("I@' 86hSeng Kim Hout and Pech BunnatKHStung / Chi Kreng / Kampong Svay GrasslandsStung / Chi Kreng / Kampong Svay GrasslandsCambodiaKampong Thom and Siem Reap ProvincesStung & Kampong Svay Districts ; Chi Kreng DistrictANE@uBiome12A1Biome12-Bengal FloricanA1 & A3@tuiiiii`;;7.."" ]]Y:҆(!I@(T .hSeng Kim Hout and Pech BunnatKHKampong TrachKampong TrachCambodiaKampot ProvinceKampong Trach DistrictANE@oA1A4iA4i-Sarus CraneA1 & A4i]@m{l]]Y:( I@"A) */g =Seng Kim Hout and Pech BunnatKHKoh Rong ArchipelagoKoh Rong ArchipelagoCambodiaSihanoukville ProvinceMittapheap DistrictANEg@pA1A1=Malaysian PloverA1X@c@ss]]Y:(I@# 4gSeng Kim Hout and Pech BunnatKHKoh Tang ArchipelagoKoh Tang ArchipelagoCambodiaSihanoukville ProvinceMittapheap DistrictANEG@pA14@aA1X@c@ss]]Y:(I@ 7h7TSeng Kim Hout and Pech BunnatKHPhnom AuralPhnom AuralCambodiaPursat, Kampong Speu & Kampong Chhnang ProvincesKravanh District ; Aural District ; Tuk Phos DistrictANE=@pSA85Biome11A1>@aA1 & A2@]p@ `@sI=111% xj]]Y:( I@^ )i(Seng Kim Hout and Pech BunnatKHNorthern SantukNorthern SantukCambodiaKampong Thom ProvinceSantuk, Stung Sen & Prasat Sambour DistrictsANE@vBiome12A1A4iA1-Greater AdjutantA1, A3 & A4i@@s-!!!!!n]]Y:҇( I@ $h&7Seng Kim Hout and Pech BunnatKHVeal SrongaeVeal SrongaeCambodiaKampong Chhnang & Kampong Thom ProvincesKampong Leng District ; Kampong Svay DistrictANE@WBiome12A1A4iM@aA1, A3 & A4iW@]@w2&&&& yk]]Y:ҏ( I@? :k/\Seng Kim Hout and Pech BunnatKHUpper Srepok CatchmentUpper Srepok CatchmentCambodiaRatanakiri & Mondulkiri ProvincesLomphat & Ya Dav Districts ; Koh Nhek & Pich Roda DistrictsANESA1A4iV@aA1, A3 & A4i@]B@c@ `@@V\PDD8,    u]]Y:( D@ -g(9Seng Kim Hout and Pech BunnatKHSre AmbelSre AmbelCambodiaKoh Kong ProvinceSre Ambel DistrictANES@QA1B@aA1,@]!River Terrapin (Batagur baska).B@P}sh]]Y:(@1@/ g8,hSeng Kim Hout and Pech BunnatKHKiriromKiriromCambodiaKoh Kong & Kampong Speu ProvincesSre Ambel & Kampong Seila Districts ; Phnom Sruoch DistrictANESg@KSA85Biome11A1k@aA1 & A3@],@ cBlack Pine (Pinus merkusii).a@ `g@JocW-! yof]]Y:(4@ + f:4USeng Kim Hout and Pech BunnatKHPhnom SamkosPhnom SamkosCambodiaPursat, Battambang & Koh Kong ProvincesKravanh District ; Samlot District ; Mondul Sema DistrictANES@HSA85Biome08A1z@aA1, A2 & A3{@]a@`@wK?333' yk]]Y: LVAL 33-34P Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone desert33-34P Oases33-34C Oases&33-34P Polar desert&33-34C Polar desertD33-34P Sea cliffs and rocky shoresD33-34C Sea cliffs and rocky shores<33-34P Rock stacks and islands<33-34C Rock stacks and islandsJ33-34P Inland cliffs and rocky slopesJ33-34C Inland cliffs and rocky slopes233-34P Scree and boulders233-34C Scree and boulders33-34P Caves33-34C Caves$33-34P Arable land$33-34C Arable land&33-34P Rice paddies&33-34C Rice paddies833-34P Improved pasture land833-34C Improved pasture landV33-34P Perennial crops, orchards and grovesV33-34C Perennial crops, orchards and groves^33-34P Forestry and agro-industrial plantations^33-34C Forestry and agro-industrial plantationsN33-34P - Current ranger patrolling and enforcement initiatives in Kirirom National Park focused on illegal activities (hunting and logging) should be continued and increased to cover all important areas. - In the area under concession, critical areas for key species in the concession should be designated in the- Current ranger patrolling and enforcement initiatives in Kirirom National Park focused on illegal activities (hunting and logging) should be continued and increased to cover all important areas. - In the area under concession, critical areas for key species in the concession should be designated in the concession management plan as special protection areas for biodiversity conservation and it should be ensured that they are not logged or disturbed. - Ongoing education and awareness initiatives focusing on day visiting tourists from Phnom Penh should be expanded and bird conservation issues highlighted. LVAL forest:33-34C Moist deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-3The IBA comprises of Kirirom National Park, together with a contiguous area of natural habitat to the west. The topography of the national park is dominated by a low massif, which rises sharply from the surrounding, densely populated lowlands to 900 m asl. The most extensive vegetation type within the national park is natural coniferous forest dominated by Pinus merkusii and with an open, grassy understorey, which is distributed on an undulating plateau, at approximately 700 m asl. The national park also supports semi-evergreen forest, and, at lower elevations, mixed deciduous forest and deciduous dipterocarp forest. There are many small streams within the national park and several artificial lakes but no major rivers. The contiguous area of natural habitat to the west of the national park is within a foresThe IBA comprises of Kirirom National Park, together with a contiguous area of natural habitat to the west. The topography of the national park is dominated by a low massif, which rises sharply from the surrounding, densely populated lowlands to 900 m asl. The most extensive vegetation type within the national park is natural coniferous forest dominated by Pinus merkusii and with an open, grassy understorey, which is distributed on an undulating plateau, at approximately 700 m asl. The national park also supports semi-evergreen forest, and, at lower elevations, mixed deciduous forest and deciduous dipterocarp forest. There are many small streams within the national park and several artificial lakes but no major rivers. The contiguous area of natural habitat to the west of the national park is within a forest concession, under the management of Samling International. This area comprises extensive semi-evergreen forest with smaller patches of coniferous forest, distributed on a series of steep hills, which rise to over 800 m asl. The area is drained by a number of small streams, which feed two larger rivers. As a result of habitat degradation and unsustainable hunting pressure, the avifauna of the IBA is less intact than that of a number of other sites in the Elephant and Cardamom Mountains. However, the IBA is the only site in Cambodia from where there are records of Brown Hornbill Anorrhinus tickelli. In addition, Lesser Fish Eagle Ichthyophaga humilis occurs along the rivers in the area to the west of the national park, and there are unconfirmed records of Chestnut-headed Partridge Arborophila cambodiana.hB  p @  P 4P Riverine floodplains633-34C Riverine floodplainsB_]UUUuUUuwUU_]UUUUuUUUwUUU _]UUUUuUUUUUUuU _]UUUUUUUUuUUuU UUUUUUuWUUwuUUU]UUUUuUUU_uUU_]UUUUUUUUwUUUUUUUUUUUUUuwuUUUUUUUUUUuWUuwuUUUUUUWUUUUu]UUuUUUUWUUUUu]_UUUUUUWUUUUUUUUuUUUUWUWUUUuU]UUUUUhB  p @  P  forest&33-34C Thorn forest.33-34P Mangroove forest.WUUUUUuWUUUUUUUUUUUUuUUuwuUU_]UUUUUUUUwUUuUUWUUUuu]_UUUW]WUUuUUUu_UUUU_]UUUUUUuwUUUUUUUUUuWUuUUUUUUUUUuWUuwuUUUU_]UUUUuUUUwUUU_]UUUUuWUwUUU_]UUUUuUUwUUU_]UUUuUUwUUUUUUUUUuWUuwuUUhB  p @  P nd streams233-34C Rivers and streams633-34P Riverine-_]UUUuWUwUU,UUUUUUuWUuwuUU+UUUUUUuUUUUUuUUUU)_]UUUUUUUUUUUuU&UUUUUUUWUuwuUU%UUUUUUuUWUuwuUU$UUUUUUUUUUuwuUUUU#_]UUUUuUUuwUUU"UUUUUUuWUuWUUU!UUUUUUUW_U}]UU WUUUUUUUWUUU]UWUUUUUUU}WUUU]UU_]UUUuUUuwUUuUBgreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest steppe(33-34C Forest steppe(33-34P Forest tundra(33-34C Forest tundra@33-34P Temperate heath and scrub@33-34C Temperate heath and scrub033-34P Semi-desert scrub033-34C Semi-desert scrubB33-34P Subalpine and alpine scrubB33-34C Subalpine and alpine scrub,33-34P Secondary scrub,33-34C Secondary scrub.33-34P Wooded grassland.33-34C Wooded grassland33-34P Tundra33-34C Tundra33-34P Steppe33-34C Steppe033-34P Edaphic grassland033-34C Edaphic grasslandJ33-34P Alpine and subalpine grasslandJ33-34C Alpine and subalpine grassland433-34P Secondary grassland433-34C Secondary grasslandd33-34P Shallow marine waters, corel reefs and keysd33-34C Shallow marine waters, corel reefs and keys"33-34P Sea inlets"33-34C Sea inlets33-34P Open sea33-34C Open sea*33-34P Estuary waters*33-34C Estuary watersN33-34P Internal mud, sand or salt flatsP33-34C Internal mud, sand or salt flats*33-34P Costal lagoons*33-34C Costal lagoons:33-34P Sand d._]UUUUuWUUUUUU LVAL 33-34P Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone desert33-34P Oases33-34C Oases&33-34P Polar desert&33-34C Polar desertD33-34P Sea cliffs and rocky shoresD33-34C Sea cliffs and rocky shores<33-34P Rock stacks and islands<33-34C Rock stacks and islandsJ33-34P Inland cliffs and rocky slopesJ33-34C Inland cliffs and rocky slopes233-34P Scree and boulders233-34C Scree and boulders33-34P Caves33-34C Caves$33-34P Arable land$33-34C Arable land&33-34P Rice paddies&33-34C Rice paddies833-34P Improved pasture land833-34C Improved pasture landV33-34P Perennial crops, orchards and grovesV33-34C Perennial crops, orchards and groves^33-34P Forestry and agro-industrial plantations^33-34C Forestry and agro-industrial plantationsN33-34P Small settlements, rural gardensN33-3- Further surveys need to be carried out focusing on identifying important sites for large waterbirds within the remaining areas of lowland coastal forest (mangrove, melaleuca) and wetlands. - Patrolling should be initiated within the Dong Peng Multiple Use Area to control illegal cutt- Further surveys need to be carried out focusing on identifying important sites for large waterbirds within the remaining areas of lowland coastal forest (mangrove, melaleuca) and wetlands. - Patrolling should be initiated within the Dong Peng Multiple Use Area to control illegal cutting and clearance of mangrove and melaleuca and hunting of large waterbirds. - An assessment should be carried out of the feasibility of including large waterbird conservation in the current initiative (education, awareness and enforcement) to protect Estuarine Terrapins (Batagur baska). LVAL forest:33-34C Moist deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.3The IBA is comprised of the estuary of the Sre Ambel River, and the associated wetland habitats. The vegetation of the IBA comprises an area of intertidal mudflats and mangrove, backed by an extensive area of Melaleuca swamp, which contains numerous small wetlands. Although the IBA has received little recent ornithological study, a range of large waterbirds in small numbers, including Milky Stork Mycteria cinerea, Painted Stork Mycteria leucocephala, Woolly-necked Stork Ciconia episcopus, Black-necked The IBA is comprised of the estuary of the Sre Ambel River, and the associated wetland habitats. The vegetation of the IBA comprises an area of intertidal mudflats and mangrove, backed by an extensive area of Melaleuca swamp, which contains numerous small wetlands. Although the IBA has received little recent ornithological study, a range of large waterbirds in small numbers, including Milky Stork Mycteria cinerea, Painted Stork Mycteria leucocephala, Woolly-necked Stork Ciconia episcopus, Black-necked Stork Ephippiorhynchus asiaticus and Lesser Adjutant Leptoptilos javanicus. Perhaps most notably, the IBA supports a small non-breeding population of Sarus Crane Grus antigone. In addition, there are historical records of both Giant and White-shouldered Ibises Pseudibis gigantea and P. davisoni from what is believed to be the general vicinity of the IBA, although there are no recent records. The IBA is included within Dong Peng Multiple Use Area, designated under the 1993 Royal Decree on Protected Areas. B @ @ @ @ @LLLLLLLL L L  L L L MMMMMMMMMM M M M NN N!N"N#N$N%N&N)N +N ,N -N .Oermanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone desert33-34P Oases33-34C Oases&33-34P Polar desert&33-34C Polar desertD33-34P Sea cliffs and rocky shoresD33-34C Sea cliffs and rocky shores<33-34P Rock stacks and islands<33-34C Rock stacks and islandsJ33-34P Inland cliffs and rocky slopesJ33-34C Inland cliffs and rocky slopes233-34P Scree and boulders233-34C Scree and boulders33-34P Caves33-34C Caves$33-34P Arable land$33-34C Arable land&33-34P Rice paddies&33-34C Rice paddies833-34P Improved pasture landsea33-34C Open sea*33-34P Estuary waters*33-34C Estuary watersN33-34P Internal mud, sand or salt flatsP33-34C Internal mud, sand or salt flats*33-34P Costal lagoons*33-34C Costal lagoons:33-34P Sand dunes and beaches:33-34C Sand dunes and beaches@33-34P Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland deltatFFFFFFFFFFF ,u@,u@~sq_rR Secondary SpeciesPPPPPPPPPPP ,u@,u@~sq_rR ReferencesBBBBBBBBBBB ,u@,u@~sq_rR IBA Site AccountNNNNNNNNNNN ,u@,u@~sq_rProtected Area Table subreportfffffffffff p۽,u@p۽,u@~sq_rPrint Report IBAJJJJJJJJJJJ ~p۽,u@p۽,u@~sq_rNew IBA report formatTTTTTTTTTTT }p۽,u@p۽,u@~sq_rLanduse Table subreportXXXXXXXXXXX |p۽,u@p۽,u@~sq_rKey Reference Table subreportddddddddddd {p۽,u@p۽,u@~sq_rIntervention Table subreportbbbbbbbbbbb zp۽,u@p۽,u@~sq_rIBA Data Form QueryPPPPPPPPPPP LVALacTThe IBA is primarily comprised of the catchment of the Srepok River upstream of Lomphat town, excluding a few peripheral areas that are heavily degraded. The topography of the IBA is relatively flat, although there are a number of low hills, most notably those around Phnom Yang Ke. The vegetation of the IBA is characterised by a habitat mosaic dominated by deciduous dipterocarp forest, with smaller areas of semi-evergreen forest and mixed deciduous forest. In addition, the IBA contains numerous wetlands. In addition to the Srepok River, its permanent tributaries and associated oxbow lakes, there are numerous seasonal streams, some of which retain pools of water during the dry season. There are also numerous pools and seasonally wet meadows, which vary in size from a few metres to a few hundreds of metres in width. The north-western part of the IBA is included within Lomphat Wildlife Sanctuary, while the southern part is included within a recently decreed Forest Reserve for Conservation of Genetic and Wildlife Resources. The IBA supports one of the most intact remaining examples of the bird community of the dry forests of central Indochina. The relative abundance of large ungulates means that the IBA has greater potential to support viable populations of White-rumped, Long-billed and Red-headed Vultures Gyps bengalensis, G. indicus and Sarcogyps calvus than most other areas in mainland South-east Asia. In addition, the Srepok River is one of the few sites in Cambodia known to support Masked Finfoot Heliopais personata. Furthermore, there is a single record of White-winged Duck Cairina scutulata from the IBA, and the presence of significant areas of suitable habitat indicate that the IBA may support a significant population of this species. There is also a single record of White-shouldered Ibis Pseudibis davisoni but the precise status of this species at the IBA is not known. Finally, there is a single record of Pale-capped Pigeon Columba punicea from along the Dak Dam stream, which forms the intern LVALiduous forest:33-34C Moist deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest steppe(33-34C Forest steppe(33-34P Forest tundra(33-34C Forest tundra@33-34P Temperate heath and scrub@33-34C Temperate heath and scrub033-34P Semi-desert scrub033-34C Semi-desert scrubB33-34P Subalpine and alpine scrubB33-34C Subalpine and alpine scrub,33-34P Secondary scrub,33-34C Secondary scrub.33-34P Wooded grassland.33-34C Wooded grassland33-34P Tundra33-34C Tundra33-34P Steppe33-34C Steppe033-34P Edaphic grassland033-34C Edaphic grasslandJ33-34P Alpine and subalpine grasslandJ33-34C Alpine and subalpine grassland433-34P Secondary grassland433-34C Secondary grasslandd33-34P Shallow marine waters, corel reefs and keysd33-34C Shallow marine waters, corel reefs and keys"33-34P Sea inlets"33-34C Sea inleational border with Vietnam, although it is unclear exactly which stretch this record is from, and it may even be from within Snoul/Keo Sema/O Reang IBA (KH027). As with White-shouldered Ibis, the precise status of this species at the IBA is not known. B @ @ @ @ @LLLLLLLL L L  L L L MMMMMMMMMM M M M NN N!N"N#N$N%N&N)N +N ,N -N .Orgreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest steppe(33-34C Forest steppe(33-34P Forest tundra(33-34C Forest tundra@33-34P Temperate heath and scrub@33-34C Temperate heath and scrub033-34P Semi-desert scrub033-34C Semi-desert scrubB33-34P Subalpine and alpine scrubB33-34C Subalpine and alpine scrub,33-34P Secondary scrub,33-34C Secondary scrub.33-34P Wooded grassland.33-34C Wooded grassland33-34P Tundra33-34C Tundra33-34P Steppe33-34C Steppe033-34P Edaphic grassland033-34C Edaphic grasslandJ33-34P Alpine and subalpine grasslandJ33-34C Alpine and subalpine grassland433-34P Secondary grassland433-34C Secondary grasslandd33-34P Shallow marine waters, corel reefs and keysd33-34C Shallow marine waters, corel reefs and keys"33-34P Sea inlets"33-34C Sea inlets33-34P Open sea33-34C Open sea*33-34P Estuary waters*33-34C Estuary watersN33-34P Internal mud, sand or salt flatsP33-34C Internal mud, sand or salt flats*33-34P Costal lagoons*33-34C Costal lagoons:33-34P Sand dunes and beaches:33-34C Sand dunes and beaches@33-34P Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers a LVAL and beaches@33-34P Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33- Measures to counter hunting and trade of wildlife must be put in place throughout the area. This should start with setting up patrolling systems in the Mondulkiri Protected Forest. - Core areas Upper Tonle Srepok, approximately west of O Chbar, both north and south of the river, to the Vietnamese border should receive strict protection under the existing structures of the Mondulkiri Protected Forest. -Conservation of this important stretch of the Srepok River should be an integral part of management of the existing conservation areas. However, this must be viewed at the scale of the complete river system, in conjunction with the stretch within Lomphat IBA (KH024), as focusing on just one small stretch in isolation could have disastrous consequences. - Further surveys and research al- Measures to counter hunting and trade of wildlife must be put in place throughout the area. This should start with setting up patrolling systems in the Mondulkiri Protected Forest. - Core areas Upper Tonle Srepok, approximately west of O Chbar, both north and south of the river, to the Vietnamese border should receive strict protection under the existing structures of the Mondulkiri Protected Forest. -Conservation of this important stretch of the Srepok River should be an integral part of management of the existing conservation areas. However, this must be viewed at the scale of the complete river system, in conjunction with the stretch within Lomphat IBA (KH024), as focusing on just one small stretch in isolation could have disastrous consequences. - Further surveys and research along the Srepok River and its tributaries needs to be carried out. These should focus on identifying important stretches of riverine forest, smaller backwater rivers and streams, and better determining the numbers and breeding success of sandbar-nesting species. - Efforts must be made to protect sandbar-nesting bird species while they are breeding. Community agreements could be set up with individual villages so that the nest areas will not be disturbed. - Immigration, illegal settlement and land encroachment into the most important and critical areas across the IBA should be prevented. - New villages and agricultural development along the Srepok River should be discouraged and key stretches of riverine forest identified should be strictly protected from logging and shifting cultivation. LVAL st deciduous forest:33-34C Moist deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline fThe IBA is an area of seasonally inundated grassland, dominated by Wild Rice Oryza rufipogon, located within the inundation zone of Tonle Sap Lake, along the border between Kampong Thom and Kampong Chhnang Provinces. The seasonally inundated grassland is surrounded by dense tall scrub and swamp forest and there are numerous seasonal pools and lakes. The southern part of the IBA is situated within Tonle Sap Multiple Use Area, designated under the 1993 Royal Decree on Protected Areas, and Tonle Sap BioThe IBA is an area of seasonally inundated grassland, dominated by Wild Rice Oryza rufipogon, located within the inundation zone of Tonle Sap Lake, along the border between Kampong Thom and Kampong Chhnang Provinces. The seasonally inundated grassland is surrounded by dense tall scrub and swamp forest and there are numerous seasonal pools and lakes. The southern part of the IBA is situated within Tonle Sap Multiple Use Area, designated under the 1993 Royal Decree on Protected Areas, and Tonle Sap Biosphere Reserve. During the dry season, the IBA supports a breeding population of Bengal Florican Houbaropsis bengalensis. Also during the dry season, the IBA is visited by a number of non-breeding large waterbirds, including Painted Stork Mycteria leucocephala, Asian Openbill Anastomus oscitans, Lesser Adjutant Leptoptilos javanicus and Greater Adjutant L. dubius. In addition, White-shouldered Ibis Pseudibis davisoni has been recorded at the IBA, although the precise status of this species is unclear.aLVALqand beaches@33-34P Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artis and islands     Yes/No  jB<33-34C Rock stacks and islands      0  mPJ33-34P Inland cliffs and rocky slopes     Yes/No  jPJ33-34C Inland cliffs and rocky slopes      0  m8233-34P Scree and boulders     Yes/No  j8233-34C Scree and boulders      0  ml33-34P Caves     Yes/No  jk33-34C Caves      0  mx*$33-34P Arable land     Yes/No  jw*$33-34C Arable land      0  mz,&33-34P Rice paddies     Yes/No  jy,&33-34C Rice paddies      0  m>833-34P Improved pasture land     Yes/No  j>833-34C Improved pasture land      0  m\V33-34P Perennial crops, orchards and groves     Yes/No  j\V33-34C Perennial crops, orchards and groves      0  md^33-34P Forestry and agro-industrial plantations     Yes/No  jd^33-34C Forestry and agro-industrial plantations      0  mTN33-34P Small settlements, rural gardens     Yes/No  jTN33-34C Small settlements, rural gardens      0  mx*$33-34P Urban areas     Yes/No  jw*$33-34C Urban areas      0  mZT33-34P Abandoned farmland, disturbed grand     Yes/No  jZT33-34C Abandoned farmland, disturbed grand      0  mM ID      m[ Y(.N(( [[((Y Y  Y dY  Y dY  Y  Y d Y d Y   Y   Y  Y   Y  Y  Y  Y    Y  Y  $Y  (Y  , Y  nY  0Y  4Y  Y  Y   Y  3 Y  u Y  ad Y id Y o Y ! x Y!" y Y"# id Y#$ n Y$%  Y%& r Y&'  Y'( Serial numberVersion1 Compiler 2 Date4 Country Code(4 Temporary IBA Code 5 Final IBA Code(6 National Site Name27 International Site Name8 CountryB9 Administrative Region (Level 1)D10 Administrative Region (Level 2)11 Area 12 Area Accuracy813 Central Coordinates Lat 1813 Central Coordinates Lat 2813 Central Coordinates Lat 4813 Central Coordinates Lat 3813 Central Coordinates Lon 1813 Central Coordinates Lon 2813 Central Coordinates Lon 4813 Central Coordinates Lon 314 Altitude Min14 Altitude Max.15 Map 1 Known Boundary615 Map 2 Digitized Boundary$16 Management Plan17 Ownership,18 General Description(19 EBA Code Proposed,20 Biome Code Proposed.21 Criteria Proposed A1.21 Criteria Proposed A4"22 Criteria NotesT66 Secondary criteria proposed for the IBAL67 Globally threatened primate speciesf68 Globally threatened turtle and crocodile speciesR69 Globally threatened gymnosperm speciesh70 Globally threatened elephant and ungulate species$71 RecommendationsY[}wY"YBYYYY$Y0YMY.rB.rC.rD.rE.rF.rG.rH.rIPrimaryKey[[![[#[[$[ [% [ [& [ ['[[ ~p۽,u@p۽,u@~sq_rNew IBA report formatTTTTTTTTTTT }p۽,u@p۽,u@~sq_rLanduse Table subreportXXXXXXXXXXX |p۽,u@p۽,u@~sq_rKey Reference Table subreportddddddddddd {p۽,u@p۽,u@~sq_rIntervention Table subreportbbbbbbbbbbb zp۽,u@p۽,u@~sq_rIBA Data Form QueryPPPPPPPPPPP ; v1b N  : k Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest steppe(33-34C Forest steppe(33-34P Forest tundra(33-34C Forest tundra@33-34P Temperate heath and scrub@33-34C Temperate heath and scrub033-34P Semi-desert scrub033-34C Semi-desert scrubB33-34P Subalpine and alpine scrubB33-34C Subalpine and alpine scrub,33-34P Secondary scrub,33-34C Secondary scrub.33-34P Wooded grassland.33-34C Wooded grassland33-34P Tundra33-34C Tundra33-34P Steppe33-34C Steppe033-34P Edaphic grassland033-34C Edaphic grass @A$@A $  @T  @gULVAL  ma233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Arti- The current conservation initiative with the local conservation team protecting the bird colonies should be further supported and expanded through the recruitment of additional village personnel and the supply of further training and resources. - The Prek Toal Core Area should be removed from the fishing lot system and give conservation status as a Fish Sanctuary under the Fisheries Law. - Appropriate Government personnel should work with the local conservation team to control illegal hunting and fishing activities in the Prek Toal Core Area by enforcing both the Forestry and Fisherie- The current conservation initiative with the local conservation team protecting the bird colonies should be further supported and expanded through the recruitment of additional village personnel and the supply of further training and resources. - The Prek Toal Core Area should be removed from the fishing lot system and give conservation status as a Fish Sanctuary under the Fisheries Law. - Appropriate Government personnel should work with the local conservation team to control illegal hunting and fishing activities in the Prek Toal Core Area by enforcing both the Forestry and Fisheries law. - Work with the local authorities to establish rules and structures for ecotourism, particularly focusing on minimizing disturbance to the colonies and distributing proceeds equitably within the local community. - Current environmental education initiatives working with both adults and children, but particularly through the local schools should be further supported and expanded into all communities in the area. - Further survey and research should be initiated to identify key feeding areas during the breeding season and to establish a long-term monitoring program for bird numbers.- Ensure all environmental impacts are fully examined and understood before there is any further conversion of mangrove and associated wetlands into agricultural land. - Further surveys need to be carried in the mudflat and mangrove areas focusing on identifying and better understanding important areas and the use of the site by both large waterbirds and migratory shorebirds.- Increase patrolling along within the Peam Krasop Wildlife Sanctuary and Koh Kapik Ramsar Site to control illegal cutting and clearance of mangrove and hunting of shorebirds. - Continue to eliminate illegal charcoal kilns in and around the area. - Carry out education and extension work on wildlife hunting and the law focusing on the ethnic Cham communities. - Further surveys need to be carried out throughout the mudflat and mangrove area focusing on identifying and better understanding important sites for migratory and wintering shorebirds.- Current ranger patrolling and enforcement initiatives in Bokor National Park focused on illegal activities (hunting and logging) should be continued and increased to cover all important areas.- Increase patrolling along the Prek Taek Sap within Ream National Park to control illegal cutting and clearance of mangrove.LVALS({%# p F  YmBh*4CLong-tailed Macaque (Macaca fascicularis), Pig-tailed Macaque (Macaca nemestrina), Silvered Langur (Semnopithecus Long-tailed Macaque (Macaca fascicularis), Pig-tailed Macaque (Macaca nemestrina), Silvered Langur (Semnopithecus cristatus), Bear Macaque (Macaca arctoides), Slow Loris (Nycticebus coucang), Pileated Gibbon (Hylobates pileatus).Long-tailed Macaque (Macaca fascicularis), Silvered Langur (Semnopithecus cristatus).Long-tailed Macaque (Macaca fascicularis) (Long Kheng, Ministry of Environment, pers. comm.).Long-tailed Macaque (Macaca fascicularis), Silvered Langur (Semnopithecus cristatus). Pig-tailed Macaque (Macaca nemestrina), Slow Loris (Nycticebus coucang), Silvered Langur (Semnopithecus cristatus), Pileated Gibbon (Hylobates pileatus).Long-tailed Macaque (Macaca fascicularis), Silvered Langur (Semnopithecus cristatus).Long-tailed Macaque (Macaca fascicularis), Pig-tailed Macaque (Macaca nemestrina), Silvered Langur (Semnopithecus cristatus), Douc Langur (Pygathrix nemaeus).Long-tailed Macaque (Macaca fascicularis).Long-tailed Macaque (Macaca fascicularis), Bear Macaque (Macaca arctoides), Pig-tailed Macaque (Macaca nemestrina), Silvered Langur (Semnopithecus cristatus), Pileated Gibbon (Hylobates pileatus), Slow Loris (Nycticebus coucang). Pig-tailed Macaque (Macaca nemestrina), Silvered Langur (Semnopithecus cristatus), Pileated Gibbon (Hylobates pileatus).Long-tailed Macaque (Macaca fascicularis)Long-tailed Macaque (Macaca fascicularis), Pig-tailed Macaque (Macaca nemestrina), Slow Loris (Nycticebus coucang), Silvered Langur (Semnopithecus cristatus), Douc Langur (Pygathrix nemaeus), Silvered Langur (Semnopithecus cristatus).Long-tailed Macaque (Macaca fascicularis), Pig-tailed Macaque (Macaca nemestrina), Slow Loris (Nycticebus coucang), Silvered Langur (Semnopithecus cristatus), Pileated Gibbon (Hylobates pileatus).Long-tailed Macaque (Macaca fascicularis), Pig-tailed Macaque (Macaca nemestrina ), Slow Loris (Nycticebus coucang).Slow Loris (Nycticebus coucang), Pygmy Loris (Nycticebus pygmaeus), Long-tailed Macaque (Macaca fascicularis), Pig-tailed Macaque (Macaca nemestrina), Bear Macaque (Macaca arctoides), Silvered Langur (Semnopithecus cristatus), Douc Langur (Pygathrix nemaeus), Yellow-cheeked Gibbon (Hylobates gabriellae).Long-tailed Macaque (Macaca fascicularis), Silvered Langur (Semnopithecus cristatus).Slow Loris (Nycticebus coucang), [Pygmy Loris (Nycticebus pygmaeus)], Long-tailed Macaque (Macaca fascicularis), Pig-tailed Macaque (Macaca nemestrina),Bear Macaque (Macaca arctoides), Douc Langur (Pygathrix nemaeus), Yellow-cheeked Gibbon (Hylobates gabriellae ) (Kong Kim Sreng pers. comm.).Pig-tailed Macaque (Macaca nemestrina) (Kong Kim Sreng pers. comm.), Pygmy Loris (Nycticebus pygmaeus), Long-tailed Macaque (Macaca fascicularis), Bear Macaque (Macaca arctoides), Douc Langur (Pygathrix nemaeus), Pig-tailed Macaque (Macaca nemestrina), Silvered Langur (Semnopithecus cristatus).Long-tailed Macaque (Macaca fascicularis), ang Silvered Langur (Semnopithecus cristatus).Long-tailed Macaque (Macaca fascicularis)[Long-tailed Macaque (Macaca fascicularis)]Slow Loris (Nycticebus coucang), Pig-tailed Macaque (Macaca nemestrina), Long-tailed Macaque( M. fascicularis), Silvered Langur (Semnopithecus cristatus) and Pileated Gibbon (Hylobates pileatus) (Mr. Song Chansocheat, Ministry of Environment, pers. comm.).Long-tailed Macaque (Macaca fascicularis), Silvered Langur (Semnopithecus cristatus)Silvered Langur (Semnopithecus cristatus), Long-tailed Macaque (Macaca fascicularis), Slow Loris (Nycticebus coucang) (Long Kheng, Ministry of Environment, pers. comm.).Long-tailed Macaque (Macaca fascicularis)Pileated Gibbon (Hylobates pileatus), Pig-tailed Macaque (Macaca nemestrina), Slow Loris (Nycticebus coucang) (Net Neath 2001).Long-tailed Macaque (Macaca fascicularis)LVAL %hingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsBThe IBA is located within Bokor National Park in the Elephant Mountains. The national park lies between Road No. 4 and the southern coastline of Cambodia. The topography of the national park is dominated by a large massif, with an extensive plateau at around 1,000 m asl. The IBA comprises all parts of the national park of semi-evergreen and evergreen forest above 400 m asl, which is thought to be the lower altitudinal limit of Chestnut-headed Partridge Arborophila cambodiana, as well as lower elevation areas along the Teuk Chhou River, which supports Lesser Fish Eagle Ichthyophaga humilis. The vegetation of the plateau is dominated by dwarf evergreen forest, with some small, cleared areas The IBA is located within Bokor National Park in the Elephant Mountains. The national park lies between Road No. 4 and the southern coastline of Cambodia. The topography of the national park is dominated by a large massif, with an extensive plateau at around 1,000 m asl. The IBA comprises all parts of the national park of semi-evergreen and evergreen forest above 400 m asl, which is thought to be the lower altitudinal limit of Chestnut-headed Partridge Arborophila cambodiana, as well as lower elevation areas along the Teuk Chhou River, which supports Lesser Fish Eagle Ichthyophaga humilis. The vegetation of the plateau is dominated by dwarf evergreen forest, with some small, cleared areas of grassland and small, artificial wetlands. The plateau is fringed by steep escarpments, hills and ridges, cloaked in semi-evergreen forest. A large river, the Teuk Chhou drains to the south and reaches the sea at Kampot town. Many smaller streams also occur throughout the area. The IBA supports Chestnut-headed Partridge one of the two restricted-range species found in the Cambodia-Thailand-Mountains Endemic Bird Area. In addition, there is a single historical record of Silver Oriole Oriolus mellianus, from 1927; which remains the only Cambodian record of this globally vulnerable species. However, the possibility exists that the species still occurs as a non-breeding visitor to the IBA.The IBA comprises the estuary of the Taek Sap River, which flows into the Gulf of Thailand to the east of Ream National Park. At the mouth of the estuary is situated a large island, called Koh Thmei. The vegetation of the IBA is dominated by intertidal mudflats and coastal mangrove, with some stands of Nypa and areas of degraded Melaleuca forest on the landward side of the mangrove. The IBA is a non-breeding site for a number of large waterbirds, including Lesser Adjutant Leptoptilos javanicus, Painted Stork Mycteria leucocephala and Spot-billed Pelican Pelecanus philippensis. Most significantly, the IBA is the most important known non-breeding site in Cambodia for Milky Stork Mycteria cinerea, which breeds at Prek Toal IBA, and most probably at an as yet undiscovered location in south-west Cambodia, quite possibly nearby (perhaps even within) this IBA.Z  d  /deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34( @-F &i:Seng Kim Hout, Keo Omaliss and Colin PooleKHMekong River from Kratie Town to LaosMekong River from Kratie Town to LaosCambodiaStung Treng & Kratie ProvincesThala Bariwatt, Stung Treng & Siem Bok Districts ; Sambo DistrictANEShA1)@aA1 & A2+@]Y@c>@jvjjj^RI==999-+)'%jjf:( @  g  Seng Kim Hout and Pech BunnatKHPreah Net Preah-Kra Lanh-PoukPreah Net Preah-Kra Lanh-PoukCambodiaSiem Reap & Banteay Meanchey ProvincesKra Lanh & Pourk Districts ; Preah Net Preah DistrictANES@fBiome12A1A4i@aA1, A3 & A4iH@ePDDDDD6*%!  |]]Y:ڇ( @s1 26gSeng Kim Hout, Keo Omaliss and Colin PooleKHAng Tropeang ThmorAng Tropeang ThmorCambodiaBanteay Meanchay ProvincePhnom Srok DistrictANESgBiome09A1A4ij@aA1, A3, A4i & A4iii-@]@cEld's Deer (Cervus eldii)C@e^R++~jjf:(@*: :i.Seng Kim Hout and Pech BunnatKHO SkachO SkachCambodiaPreah Vihear ProvinceChhep, Chom Khsan & Tbeng Meanchey DistrictsANESi@fBiome11A1A4iA1 & A4i@]/@c@`@@eyof]]Y:(@ 22h Seng Kim Hout, Keo Omaliss and Colin PooleKHBoeung Chhmar / Moat KhlaBoeung Chhmar / Moat KhlaCambodiaKampong Thom & Siem Reap ProvincesStung District ; Chikreng & Sotr Nikum DistrictsANES@dA1A4i%@aA1, A4i & A4iiiV@]@cc@e^RRRF:)jjf:(@  g'Seng Kim Hout, Keo Omaliss and Colin PooleKHPrek ToalPrek ToalCambodiaBattambang ProvinceEk Phnom, Sangke & Mong Russey DistrictsANES@dA1A4i&@aA1, A4i & A4iii@]@c@\'ujjf:(@ 5 $6g25Seng Kim Hout, Keo Omaliss and Colin PooleKHStung Kampong SmachStung Kampong SmachCambodiaKampot & Sihanoukville ProvincesKampot District ; Prey Nup DistrictANE@bA1*@aA1}@\     jjf:(@j g nSeng Kim Hout, Keo Omaliss and Colin PooleKHKoh KapikKoh KapikCambodiaKoh Kong ProvinceKoh Kong, Smach Meanchey & Mondul Sema DistrictsANESo@bA1A4i 13 Nordmann's Greenshank (A4i)A1 & A4i+@])@\:...."ujjf:(@ӌ 21h! 9Seng Kim Hout, Keo Omaliss and Colin PooleKHPhnom BokorPhnom BokorCambodiaKampot, Sihanoukville & Koh Kong ProvincesKampot District ; Prey Nup District ; Kampong Seila DistrictANESx@^SA85Biome09A1a@aA1, A2 & A3@]No information.Noner@`@\saD8+ wjjf:(@! "g)oSeng Kim Hout, Keo Omaliss and Colin PooleKHPrek Taek SapPrek Taek SapCambodiaSihanoukville ProvincePrey Nup DistrictANESc@^Biome09A1A4iA4i 22 Greater Adjutants.A1 & A4i+@]@\,     yjjf:ڏ LVALO < j  _ elta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone desert33-34P Oases33-34C Oases&33-34P Polar desert&33-34C Polar desertD33-34P Sea cliffs and rocky shoresD33-34C Sea cliffs and rocky shores<33-34P Rock stacks and islands<33-34C Rock stacks and islandsJ33-34P Inland cliffs and rocky slopesJ33-34C Inland cliffs and rocky slopes233-34P Scree and boulders233-34C Scree and boulders33-34P Caves33-34C Caves$33-34P Arable land$33-34C Arable land&33-34P Rice paddies&33-34C Rice paddies833-34P Improved pasture land833-34C Improved pasture landV33-34P Perennial crops, orchards and grovesV33-34C Perennial crops, orchardsAsian Elephant (Elephas maximus), Gaur (Bos gauAsian Elephant (Elephas maximus), Gaur (Bos gaurus), Southern Serow (Naemorhedus sumatraensis).Banteng (Bos javanicus), Gaur (Bos gaurus), Eld's Deer (Cervus eldii).Asian Elephant (Elephas maximus), Gaur (Bos gaurus), (Song Chansocheat, Ministry of Environment, pers. comm.).Asian Elephant (Elephas maximus), Eld's Deer (Cervus eldii), Gaur (Bos gaurus), Banteng (Bos javanicus) and Wild Water Buffalo (Bubalus arnee).Asian Elephant (Elephas maximus), Gaur (Bos gaurus), Southern Serow (Naemorhedus sumatraensis).Asian Elephant (Elephas maximus), Gaur (Bos gaurus), Southern Serow (Naemorhedus sumatraensis).Asian Elephant (Elephas maximus), Gaur (Bos gaurus) and Banteng ( B. javanicus).Gaur (Bos gaurus), Banteng (Bos javanicus), Eld's Deer (Cervus eldii) (Kong Kim Sreng, Ministry of Environment, pers. comm.).Asian Elephant (Elephas maximus), Banteng (Bos javanicus), Gaur (Bos gaurus), Eld's Deer (Cervus eldii).Asian Elephant( Elephas maximus), Gaur (Bos gaurus), Banteng (Bos javanicus), Southern Serow (Naemorthedus sumatraensis), [Giant Muntjac (Megamuntiacus vuquangensis)].Asian Elephant (Elephas maximus), Gaur (Bos gaurus), Banteng (Bos javanicus).Asian Elephant (Elephas maximus), Eld's Deer (Cervus eldii), Gaur (Bos gaurus), Banteng (Bos javanicus).Asian Elephant (Elepas maximus), Banteng (Bos javanicus), Gaur (Bos gaurus) (Prum Sovanna, Wildlife Protection Office, pers. comm.).Asian Elephant (Elephas maximus), Gaur (Bos gaurus), Southern Serow (Naemorhedus sumatraensis) (Net Neath 2001).LVALuO* F w U-YV K en forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C MontaA1=Lesser Adjutant and PaintedA1=Lesser Adjutant and Painted Stork Biome12=Bengal FloricanA1=Great Hornbill, Chestnut-headed Partridge A2=Chestnut-headed PartridgeA1=Christmas island Frigatebird and Nicobar PigeonSA085-Chestnut-headed Partridge and Cambodian LaughingthrushA4i-168 Lesser Adjutants and 1000 Intermediate Egrets. B12- Bengal FloricanA1-Giant Ibis, White-shouldered Ibis, Sarus Crane, White-winged Duck, Great HornbillA1 (Sarus Crane, Milky Stork, Lesser Adjutant and Painted Stork)The Park contains the species relevant to Biome 11, Biome 09 and Biome 08 as well as S3 (Pinus merkusii).The site contains A2 (Chestnut-headed Partridge and Cambodian Laughingthrush) and bird species in Biome 08 and Biome 09.A1: Greater and Lesser Adjutants, and Grey-headed Fish-eagle. A4i: 120 Oriental DartersA1: 24 Green Peafowls A4i: Giant IbisA1: 27 Oriental Darter, 13 Lesser AdjutantContains equal species relevant to B08 and B09. A4i: 11Giant Ibis, 16 Black-necked Stork and 71 Lesser Adjutant.A1-White-winged Duck A2-Germain's Peacock Pheasant, Orange-necked Partridge Contains equal specias relevant from B08 to B012.A4i-Bengal Florican A4i-Greater Adjutant 84 birdsEBA144-Germain's Peacock Pheasant and A4i-Giant Ibis, White-shouldered Ibis, Greater Adjutant.A4i - Giant Ibis A2: Mekong Wagtail Motacilla samveasnaeA4i - Small Pratincole and River Lapwing A2: Mekong Wagtail Motacilla samveasnaeA2: Mekong Wagtail Motacilla samveasnaeCriteria A4i and A4iii unconfirmed based on villagers' reports of more than 100 Sarus Cranes and more than 115 Spot-billed Pelicans. A4iii based on villagers' reports of more than 20,000 waterfowl of unknown species. Biome 12 contains Bengal Floricans.A4i - Sarus Crane, Lesser Whistling Duck, Asian Openbill, Comb Duck and Black-necked Stork. A4iii - 25,000-30,000 waterfowl estimated in March 1998 (Sam Veasna and Mundkur 1998), mostly Lesser Whistling Duck. Two groups of 500 Egrets and "several thousand" Lesser Whistling Duck, April 1998 (Sam Veasna et al. 1998). The site is also met B08, B09 and B011.A4i- 5 species (including Black-necked Stork) see overleaf. A4iii- In addition to overleaf. Mundkur (et al. 1995) document "several thousand" Whiskered Tern, "large numbers"of Indian Cormorant and Great Egret as very common. Parr et al. (1996) recorded 3,000 Cormorant sp. And 800 Egret sp.Meets A4i for 11 species (see overleaf). A4iii see overleaf. In addition Parr et al (1996) report 1500 Lesser Whistling Ducks, Ear Dupuy et al (1997) similar numbers and 2,260 Egrets and Herons of 4 species and Chamnan (AWC 2001 unpubl) 2713 Little Cormorants and 1469 Spot-billed Pelicans.A1=Geater Adjutants and Asian DowitchersContains Equal species relevant to B08 and B09. But SA085 is only listed under B08 and not B09.mLVAL ches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&The IBA comprises the estuary of the Kampong Smach River, which flows into the Gulf of Thailand to the west of Bokor National Park. At the mouth of the river there are extensive mangroves and intertidal mudflats, while, upriver, there are stands of Melaleuca and Nypa. The mangrove along the western side of the estuary has been significantly reduced by land reclamation and conversion to rice agriculture but that on the eastern side is in a better condition, with stands of mature mangrove. The IBA is an important siThe IBA comprises the estuary of the Kampong Smach River, which flows into the Gulf of Thailand to the west of Bokor National Park. At the mouth of the river there are extensive mangroves and intertidal mudflats, while, upriver, there are stands of Melaleuca and Nypa. The mangrove along the western side of the estuary has been significantly reduced by land reclamation and conversion to rice agriculture but that on the eastern side is in a better condition, with stands of mature mangrove. The IBA is an important site for migratory waterbirds, including Asian Dowitcher Limnodromus semipalmatus. In addition, the IBA supports a number of large waterbirds during the non-breeding season, including Lesser Adjutant Leptoptilos javanicus, Painted Stork Mycteria leucocephala, Milky Stork M. cinerea and Spot-billed Pelican Pelecanus philippensis. Most signficantly, there is a record of 22 Greater Adjutant L. dubius from 1994, although there have been no subsequent records, and the species may not regularly occur in significant numbers.The IBA is situated to the south of Koh Kong provincial town, and comprises all areas of mangrove forest on Koh Kapik island and associated coastal areas on the mainland. The IBA supports the most intact mature mangrove forest in Cambodia and, arguably, in the whole of the Gulf of Thailand. The mangroves around Koh Kapik island are bisected by many creeks. Along the western coastline of the island, there are well developed mudflats, while the northern coastline is more sandy. There is a single village (Koh Kapik) on the island, where the main industry is fishing. Much of the IBA is included within Peam Krasop Wildlife Sanctuary, and the southern parts, centred on the island, have been designated as Koh Kapik Ramsar site. The IBA is an important site for migratory waterbirds, including Nordmann's Greenshank Tringa guttifer and Asian Dowitcher Limnodromus semipalmatus. In addition, there are historical records of Milky Stork Mycteria cinerea and Lesser Adjutant Leptoptilos javanicus from 1944, although there have been no recent records, and the current status of these globally vulnerable species at the IBA is unknown.gLVAL C W cxL Zo'y deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montaSiamese Crocodile (Crocodylus siamensis), Impressed Tortoise (ManoSiamese Crocodile (Crocodylus siamensis), Impressed Tortoise (Manouria impressaand) and Asiatic Softshell Turtle (Amyda cartilaginea).Asiatic Softshell Turtle (Amyda cartilaginea), Malayan Box Turtle (Cuora ambionensis), Malayan Snail-eating Turtle (Malayemys subtrijuga), Yellow-headed Temple Turtle (Hieremys annandalii), [Siamese Crocodile (Crocodylus siamensis)].Asiatic Softshell Turtle (Amyda cartilaginea), Asian Giant Softshell (Pelochelys cantorii).Asiatic Softshell Turtle (Amyda cartilaginea), Malayan Box Turtle (Cuora ambionensis), Malayan Snail-eating Turtle (Malayemys subtrijuga), Yellow-headed Temple Turtle (Hieremys annandalii), [Siamese Crocodile (Crocodylus siamensis)].Green Sea Turtle (Chelonia mydas) (Phay Somany, Department of Fisheries, pers. comm.).Green Sea Turtle (Chelonia mydas) (Phay Somany, Department of Fisheries, pers. comm.).Asiatic Softshell Turtle (Amyda cartilaginea), [Asian Giant Softshell Turtle (Pelochelys cantorii)], Yellow-headed Temple Turtle (Hieremys annandalii), Giant Asian Pond Turtle (Heosemys grandis), Elongated Tortoise (Indotestudo elongata), Malayan Box Turtle (Cuora ambionensis), Siamese Crocodile (Crocodylus siamensis).Elongated Tortoise (Indotestudo elongata).Asiatic Softshell Turtle (Amyda cartilaginea), Malayan Box Turtle (Cuora ambionensis), Malayan Snail-eating Turtle (Malayemys subtrijuga), Yellow-headed Temple Turtle (Hieremys annandalii), [Siamese Crocodile (Crocodylus siamensis)].Yellow-headed Temple Turtle (Hieremys annandalii), Elongated Tortoise (Indotestudo elongata) Malayan Box Turtle (Cuora ambionensis).Asiatic Softshell Turtle (Amyda cartilaginea), Elongated Tortoise (Indotestudo elongata), Yellow-headed Temple Turtle (Hieremys annandalii), Giant Asian Pond Turtle (Heosemys grandis), Malayan Box Turtle (Cuora ambionensis).Asiatic Softshell Turtle (Amyda cartilaginea), Elongated Tortoise (Indotestudo elongata), Yellow-headed Temple Turtle (Hieremys annandalii), Giant Asian Pond Turtle (Heosemys grandis), Malayan Box Turtle (Cuora ambionensis).Asiatic Softshell Turtle (Amyda cartilaginea), Elongated Tortoise (Indotestudo elongata), Impressed Tortoise (Manouria impressa), Malayan Box Turtle (Cuora ambionensis)Impressed Tortoise (Manouria impressa).Asiatic Softshell Turtle (Amyda cartilaginea), [Asian Giant Softshell (Pelochelys cantorii)], Elongated Tortoise (Indotestudo elongata), Yellow-headed Temple Turtle (Hieremys annandalii), Giant Asian Pond Turtle (Heosemys grandis), Siamese Crocodile (Crocodylus siamensis).Giant Asian Pond Turtle (Heosemys grandis), Siamese Crocodile (Crocodylus siamensis).Asian Giant Softshell (Pelochelys cantorii), [Siamese Crocodile (Crocodylus siamensis)]Malayan Box Turtle (Cuora ambionensis), Malayan Snail-eating Turtle (Malayemys subtrijuga), Elongated Tortoise (Indotestudo elongata).Asiatic Softshell Turtle (Amyda cartilaginea)Asiatic Softshell Turtle (Amyda cartilaginea), Malayan Box Turtle (Cuora ambionensis), Malayan Snail-eating Turtle (Malayemys subtrijuga), Yellow-headed Temple Turtle (Hieremys annandalii), Siamese Crocodile (Crocodylus siamensis).Asiatic Softshell Turtle (Amyda cartilaginea), Malayan Box Turtle (Cuora ambionensis), Malayan Snail-eating Turtle (Malayemys subtrijuga), Yellow-headed Temple Turtle (Hieremys annandalii), Siamese Crocodile (Crocodylus siamensis) (Long Kheng, Ministry of Environment, pers. comm.).LVAL^ and delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine flooThe IBA comprises of the open wetlands and swamp forest of the Boeung Chhmar Core Area of Tonle Sap Biosphere Reserve and the adjacent Moat Khla area to the north. Boeung Chhmar is a permanent, 4,000 ha lake, surrounded by flooded swamp forest, comprising tall (7-15 m high) gallery forest and fairly homogeneous stands of short (2-4 m high) trees and scrub. Boeung Chhmar is linked to Tonle Sap Lake by a maze of channels and streams. Moat Khla is an area of flooded swamp forest, characterised by a dense network of interconnected channels and shallow creeks, running parallel to the lakeshoThe IBA comprises of the open wetlands and swamp forest of the Boeung Chhmar Core Area of Tonle Sap Biosphere Reserve and the adjacent Moat Khla area to the north. Boeung Chhmar is a permanent, 4,000 ha lake, surrounded by flooded swamp forest, comprising tall (7-15 m high) gallery forest and fairly homogeneous stands of short (2-4 m high) trees and scrub. Boeung Chhmar is linked to Tonle Sap Lake by a maze of channels and streams. Moat Khla is an area of flooded swamp forest, characterised by a dense network of interconnected channels and shallow creeks, running parallel to the lakeshore, bordered by tall (7-15 m high) gallery forest, dominated by Barringtonia acutangula and Diospyros cambodiana. Boeung Chhmar has been designated as a Ramsar site. Boeung Chhmar is clearly one of the important feeding sites for large waterbirds in Cambodia, particularly in the post-breeding period, and regularly supports significant numbers of Spot-billed Pelican Pelecanus philippensis, Indian Cormorant Phalacrocorax fuscicollis, Painted Stork Mycteria leucocephala and Greater Adjutant Leptoptilos dubius. In addition, Masked Finfoot Heliopais personata has been recorded at Moat Khla.Prek Toal is one of the most intact areas of freshwater swamp forest around Tonle Sap Lake. This unique ecosystem is adapted to withstand seasonal variation of water level of up to 10 m, and consists of short-tree shrublands and gallery forests of 7-15 m tall trees, dominated by Barringtonia acutangula and Diospyros cambodiana and a variety of woody lianas. In the dry season (January to May), these large trees support the largest remaining colonies of storks, pelicans and ibises in mainland South-east Asia. The IBA is centred on the Prek Toal Core Area of Tonle Sap Biosphere Reserve and includes all areas the bird colonies and the areas of best swamp forest. It is also completely inside a fishing concession (Fishing Lot No. 2 of Battambang Province),and the area is commercially fished on an industrial scale between January and July, severely restricting access to people who are not employees of the concessionaire. The waterbird colonies of Prek Toal contain some of the world's largest numbers of Spot-billed Pelican Pelecanus philippensis and Greater Adjutant Leptoptilos dubius, and Prek Toal is perhaps the only site in world where Milky Stork Mycteria cinerea breeds in freshwater. In addition, the IBA supports significant wet season breeding populations of Darter Anhinga melanogaster and Grey-headed Fish Eagle Ichthyophaga ichthyaetus, and, Masked Finfoot Heliopais personata, young chicks of which have been recorded.LVAL ] eciduous forest633-34P Dry evergreen forest633-34C Dry everg- Law enforcement and community awareness activities should be initiated based on the successful model at Stung Sen / Santuk / Baray (IBA #21). These should focus on controlling the hunting and trade of key species, particularly Bengal Floricans and large waterbirds and the potential benefits to local communities. - Further research should be carried out on the relative ecological roles of the seasonally flooded- Law enforcement and community awareness activities should be initiated based on the successful model at Stung Sen / Santuk / Baray (IBA #21). These should focus on controlling the hunting and trade of key species, particularly Bengal Floricans and large waterbirds and the potential benefits to local communities. - Further research should be carried out on the relative ecological roles of the seasonally flooded grasslands and deep water rice areas, particularly to the conservation of Bengal Florican. - Any further agricultural development, particularly deep water rice expansion, should not be undertaken without a full environmental impact assessment and a proper understanding, based on the above, of the potential effects of conversion of the semi-natural ecosystems (upon which the floricans may be reliant) to agriculture.- Current enforcement activities at Ang Trapeang Thmor focused on controlling illegal hunting should be continued. - A management plan that zones the reserve for different land uses, particularly delimiting rice cultivation areas, should be agreed on by all stakeholders as soon as possible and strictly enforced. - Community development programs should be initiated in villages inside and adjacent to the reserve, focusing on sustainable livelihoods. - A tourism plan should be developed looking at the potential impacts of mass tourism on the reserve and the potential benefits of good management practices for local communities. -Forest clearance and land encroachment in and around the site is a complex problem at the moment, therefore land tenure agreements are necessary to facilitate effective management of the reserve.- Designate important riverine areas for White-winged Duck as special protection areas for biodiversity conservation within the concession management plan and it should be ensured that they are not further logged or disturbed. - Establish community hunting agreements limiting the use dogs, and increase village-based awareness of White-winged Duck. - Ensure that all logging activity takes place in line with legal requirements for good practice. - Concession staff and contractors should uphold the laws and guidelines preventing illegal hunting within the concession.- Enforcement activities should be undertaken by appropriate Government personnel to control illegal hunting and fishing activities, particularly in the Beong Chhma Core Area and Boeng Chhma/Moat Khla Ramsar Site. - Further surveys should be carried out to identify any, as yet undocumented, breeding colonies, particularly of Darters in the wet season and adjutants in the dry season. - Further research and survey is also required to better understand key post-breeding areas. - If appropriate initiate a local conservation program based on the successful model of Prek Toal (IBA #3) to protect key areas for breeding or feeding. - Initiate an environmental education program, based on the successful model in Prek Toal (IBA #3). This should work with both adults and children, but particularly through the local schools throughout the Boeng Chhma Core Area.LVAL  beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval andThe IBA is located in the north-western part of the Tonle Sap floodplain, and comprises a substantial area of seasonally inundated grassland and scrub. This includes, in the south-east of the IBA, an area reportedly dominated by Wild Rice Oryza rufipogon, in mosaic with tall scrub and flooded forest, similar to that found at Veal Srongae IBA (KH020). In recent years, these habitats have been increasingly converted to deepwater and recession rice, reducing and fThe IBA is located in the north-western part of the Tonle Sap floodplain, and comprises a substantial area of seasonally inundated grassland and scrub. This includes, in the south-east of the IBA, an area reportedly dominated by Wild Rice Oryza rufipogon, in mosaic with tall scrub and flooded forest, similar to that found at Veal Srongae IBA (KH020). In recent years, these habitats have been increasingly converted to deepwater and recession rice, reducing and fragmenting the key habitats at the IBA. The IBA is an important dry season breeding area for Bengal Florican Houbaropsis bengalensis, which occurs in areas of seasonally inundated grassland throughout. In addition, several other globally threatened and near-threatened species have been seasonally recorded at the IBA in small numbers, including Sarus Crane Grus antigone, Black-necked Stork Ephippiorhynchus asiaticus and Spot-billed Pelican Pelecanus philippensis.The IBA is situated in the upper catchment of the Stung Sen River, and comprises a large patch of evergreen and semi-evergreen forest, within a landscape dominated by open deciduous dipterocarp forest. The IBA contains a high density of freshwater wetlands, including rivers, streams, lakes and pools. The IBA is located within a forest concession managed by the Chendar Plywood Company, and is contiguous with the newly decreed Protected Forest for Conservation of Genetic Diversity, Vegetation and Wildlife Resources in Chhep and Chom Khsan districts. The IBA is important for the conservation of a range of forest bird species, including Green Peafowl Pavo muticus, Siamese Fireback Lophura diardi and Great Hornbill Buceros bicornis. Most notably, the IBA supports a breeding population of White-winged Duck Cairina scutulata, the most significant known in Cambodia.\LVALlciduous forest633-34P Dry deciduous forest633-The IBA comprises the Ang Tropeang Thmor Sarus Crane Conservation Area. The IBA is centred on an artificial lake, located 70 km to the north-west of Tonle Sap Lake. During the Angkorian period, from the 10th to the 13th century AD, a major causeway was constructed through the area, which led to increased water accumulation to the north. In 1976, during Pol Pot's Democratic Kampuchea regime, forced labor was used to convert an 11 km stretch of this causeway into a dam and to build a 9 km dyke perpendicular to it. However, the planned irrigation reservoir was never completed. Consequently, during the dry season, only the south-eastern corner of the reservoir remains inundated, although, at the height of the wet season, over 80% of the IBA is inundated. Seasonally inundated areas support seasonally inundated grassland, the northern portion of which is inundated for a shorter period each year and has been extensively converted to wet rice agriculture. This land has, however, only been irregularly used for a number of years. In the extreme north of the IBA, the habitat grades into open deciduous dipterocarp forest. The IBA is the most important non-breeding site for Sarus Crane Grus antigone in Cambodia and regularly supports a significant proportion of the global population of the eastern subspecies G. a. sharpii. In addition to Sarus Crane, the IBA regularly supports over 1% of the Asian biogeographic population of Lesser Whistling-duck Dendrocygna javanica, Comb Duck Sarkidiornis melanotus, Asian Openbill Anastomus oscitans and Black-necked Stork Ephippiorhynchus asiaticus. Furthermore, a large number of globally threatened and near-threatened species have been recorded at the IBA, including Bengal Florican Houbaropsis bengalensis (which probably breeds), White-shouldered Ibis Pseudibis davisoni and Greater Adjutant Leptoptilos dubius. Additionally the globally threatened Pallas s Fish Eagle Haliaeetus leucoryphus has been recorded at the site as a vagrant.LVALesiThe IBA comprises the Mekong River and associated riverine vegetation, from Kratie town to the international border with Laos. Along this stretch, the Mekong River is very varied. Some sections form a single channel, up to 1.5 km wide, with a vast expanse of open water, while other sections are braided into a number of channels and islands. In sections of braided river, several types of river channel vegetation occur: small, periodically flooded, predominantly grass-covered islands; shrubs that become partly submerged for most of the wet season; and trees in open canopy aggregations, which become partly submerged for most of the wet season. Other key habitats include sandbars and rocks. Although much of the fringing riverine forest is degraded, some areas of good condition mixed deciduous/semi-evergreen forest remain around the Kratie-Stung Treng provincial border. Away from the river, this grades into open deciduous dipterocarp forest. Many human settlements, with associated shifting cultivation, are located along the river. The stretch of the Mekong River from a point 5 km north of Stung Treng town to the international border with Laos has been designated as a Ramsar site. The IBA supports a large proportion of the global population of Mekong Wagtail Motacilla samveasnae, a recently described species, which is thought to be endemic to the Mekong River and its major tributaries. In addition, the IBA supports significant populations of a suite of riverine species that have declined severely throughout mainland South-east Asia, including River Lapwing Vanellus duvaucelii, Great Thick Knee Esacus recurvirostris and River Tern Sterna aurantia. Furthermore, a number of globally threatened and near-threatened species have been recorded at the IBA in small numbers, including White-rumped Vulture Gyps bengalensis, Red-headed Vulture Sarcogyps calvus and Darter Anhinga melanogaster. Small, but significant numbers of White-shouldered Ibis Pseudibis davisoni have been recorded along forested parts of the riv LVAL st633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest steppe(33-34C Forest steppe(33-34P Forest tundra(33-34C Forest tundra@33-34P Temperate heath and scrub@33-34C Temperate heath and scrub033-34P Semi-desert scrub033-34C Semi-desert scrubB33-34P Subalpine and alpine scrubB33-34C Subalpine and alpine scrub,33-34P Secondary scrub,33-34C Secondary scrub.33-34P Wooded grassland.33-34C Wooded grassland33-34P Tundra33-34C Tundra33-34P Steppe33-34C Steppe033-34P Edaphic grassland033-34C Edaphic grasslandJ33-34P Alpine and subalpine grasslandJ33-34C Alpine and subalpine grassland433-34P Seer. Finally, the IBA may be one of the last remaining sites in Indochina to support Black-bellied Tern Sterna acuticauda, although there have been few recent records and no recent confirmation of breeding. Historically the area supported a breeding population of Indian Skimmer Rhynchops albicollis, however, the last record on this stretch of the river was of  several pairs in 1932, and the failure to find the species on recent surveys indicate that it is probably now extinct on the Mekong River.LVAL gle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone dese- Efforts must be made to protect sandbar-nesting bird species while they are breeding. Community agreements could be set up with individual villages so that the nest areas will not be disturbed. - Conservation of the Sesan River should be at the scale of the complete length of the river system as focusing on just a small stretch in isolation could have disastrous consequenc- Efforts must be made to protect sandbar-nesting bird species while they are breeding. Community agreements could be set up with individual villages so that the nest areas will not be disturbed. - Conservation of the Sesan River should be at the scale of the complete length of the river system as focusing on just a small stretch in isolation could have disastrous consequences. - New villages and agricultural development along the river should be discouraged and key stretches of riverine forest identified should be strictly protected from logging and shifting cultivation. - Research should be carried out focusing on the effects of the Sesan Dam HEP development on the bird communities, particularly the breeding success of sandbar-nesting species.- Conservation of the stretch of the Mekong River designated as a Ramsar Site is an important priority, however, this must be viewed at the scale of the complete length of the river system IBA as focusing on just a small stretch in isolation could have disastrous consequences. - Further surveys and research need to be carried out. These should focus on identifying important stretches of riverine forest, smaller backwater rivers and streams, and better determining the numbers and breeding success of sandbar-nesting species - Efforts must be made to protect sandbar-nesting bird species while they are breeding. Community agreements could be set up with individual villages so that the nest areas will not be disturbed. - New villages and agricultural development along the river should be discouraged and key stretches of riverine forest identified should be strictly protected from logging and shifting cultivation. - Management and conservation activities of the key species of wildlife and fish should be put in place for Stung Treng and Boeung Tonle Chhma Ramsar Sites.LVAL -34C Moist deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain The IBA comprises the entire Cambodian stretch of the Sesan River and associated riverine vegetation, from its confluence with the Sekong River to the international border with Vietnam. The Sesan River is relatively wide, averaging c.150 m wide in the upper reaches and c. 300 m wide lower down. Most sections of the river are dominated by sand and gravel bars, apart from the lowest section, below Phum Khsach Thmei, which is much more rocky. In the upper reaches of the river, bars comprise mostly gravel, often with low shrub growth, while those in the lower reaches are almost entirely sand, with little or no shrub growth. The riverine vegetation is dominated by semi-evergreen and mixed deciduous forest, which grades into deciduous dipterocarp forest away from the river. The riverine vegetation is generally degraded throughout, mainly as a result of shifting cultivation. The IBA The IBA comprises the entire Cambodian stretch of the Sesan River and associated riverine vegetation, from its confluence with the Sekong River to the international border with Vietnam. The Sesan River is relatively wide, averaging c.150 m wide in the upper reaches and c. 300 m wide lower down. Most sections of the river are dominated by sand and gravel bars, apart from the lowest section, below Phum Khsach Thmei, which is much more rocky. In the upper reaches of the river, bars comprise mostly gravel, often with low shrub growth, while those in the lower reaches are almost entirely sand, with little or no shrub growth. The riverine vegetation is dominated by semi-evergreen and mixed deciduous forest, which grades into deciduous dipterocarp forest away from the river. The riverine vegetation is generally degraded throughout, mainly as a result of shifting cultivation. The IBA supports one of the best remaining examples of the riverine bird community that was once widespread along wide, lowland rivers in Indochina. This community includes River Lapwing Vanellus duvaucelii, Small Pratincole Glareola lactea, Great Thick-knee Esacus recurvirostris and River Tern Sterna aurantia, of which the IBA supports over 1% of the Asian biogeographic population of the former two. In addition, the IBA supports Mekong Wagtail Motacilla samveasnae, a recently described species, which is thought to be endemic to the Mekong River and its major tributaries. Furthermore, the IBA may be one of the last remaining sites in Indochina to support a breeding population of Black-bellied Tern Sterna acuticauda, although this is probably now limited to one or two pairs, and with changes in flow regime following the development of hydropower schemes upstream, on the verge of extinction.NZ r  S cpeaches&33-34P Inland delta&33-34C Inlan(@ @'<$ +iSeng Kimhout and Pech BunnatKHBoeung Prek LapouvBoeung Prek LapouvCambodiaTakeo ProvinceBorey Chulsar & Koh Andeth DistrictsANES@GBiome12A1A4iA4i: Sarus CraneA1, A3 & A4iu@F"p\\X:ه(,@f0 #8h Seng Kimhout and Pech BunnatKHLower Stung SenLower Stung SenCambodiaKompong Thom ProvinceKampong Svay DistrictANES@vA1A4iZ@aA1 & A4i+@]@ cs@w ~m\\X:(@  j&Seng Kim Hout and Pech BunnatKHMondulkiri / Kratie LowlandsMondulkiri / Kratie LowlandsCambodiaMondulkiri & Kratie ProvincesPich Roda & Keo Sema Districts ; Kratie & Snoul DistrictsANES@EBiome11A1A4i(@aA1, A3 & A4i@]@ cR@`A@wmaUUI=/#{]]Y:(@$h,$"Seng Kim Hout and Pech BunnatKHUpper Stung Sen CatchmentUpper Stung Sen CatchmentCambodiaPreah Vihear & Siem Reap ProvincesChom Khsan, Kulen, Tbeng Meanchey & Chey San Districts ; Svay Lue DistrictANES@DBiome11A1,@ aA1& A4i@]@ c@`@wsg[[OC:..*!! x]]Y:((@ͷi#Seng Kim Hout and Pech BunnatKHChhepChhepCambodiaPreah Vihear ProvinceChhep & Chom Khsan DistrictsANES@vBiome11A1A4it@ aA1, A3 & A4iv@ ]@ cj@`#@sukd]]Y:(@3 1k16Seng Kim Hout and Pech BunnatKHSnoul / Keo Sema / O ReangSnoul / Keo Sema / O ReangCambodiaMondulkiri & Kratie ProvincesKeo Sema & O Reang Districts ; Snoul DistrictANESqEBA144Biome08A1@ aA1, A2, A3 & A4i3@ ]@c@`@sdXLL@4" y]]Y:(!@E 6h40Seng Kim Hout and Pech BunnatKHStung Sen / Santuk / BarayStung Sen / Santuk / BarayCambodiaKampong Thom, Kampong Cham & Kampong Chhnang ProvincesKmpg. Svay, Santuk, Stung Sen & Baray Distr.; Batheay Distr.; ChulKiri & Kmpg. Leng Distr.ANESg@pBiome12A1A4i4@ aA1, A3 & A4iW@ ]$@mtfZUQHH<:864z^^Z:ڏ(@ 0k A Seng Kim Hout, Keo Omaliss and Colin PooleKHViracheyViracheyCambodiaStung Treng & Ratanakiri ProvincesSiem Pang District ; Ven Sai & Ta Veng DistrictsANES@oEBA144A1A4i`@ aA1, A2 & A4i'@ ])@cPinus merkusii.O@`@mj^R5)~tjjf:(@ݬ j&!,Seng Kim Hout, Keo Omaliss and Colin PooleKHLomphatLomphatCambodiaStung Treng, Kratie, Ratanakiri & Mondulkiri ProvincesSesan District ; Sambour District ; Kom Mum & Lomphat Districts ; Koh Nhek DistrictANES&@nA1A4i;@aA1, A2, A3 & A4i*@ ]@cj@`@m~rffZN<0+'''|sjjf:( @ P 0 k+Seng Kim Hout, Keo Omaliss and Colin PooleKHTonle SesanSesan RiverCambodiaStung Treng & Ratanakiri ProvincesSiem Pang & Sesan Districts ; Ven Sai, Ta Veng & Andong Meas DistrictsANES@kA1A4iS@aA1, A2 & A4i[@]W@c@jUIII=1#wjjf:LVAL6 uQduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34- The current law enforcement initiative focused on t- Any further irrigation or agricultural development in the area should not be undertaken without a full environmental impact assessment and a proper understanding of the po- Any further irrigation or agricultural development in the area should not be undertaken without a full environmental impact assessment and a proper understanding of the potential effects on the natural wetland upon which the cranes are reliant. - Enforcement activities should be initiated as soon as possible focusing on hunting of waterbirds.- The current law enforcement initiative focused on the hunting and trade of key species, particularly Bengal Floricans and large waterbirds should be expanded throughout the area. - The current community awareness initiative begun in Krous Kraom and adjacent areas should be expanded throughout the IBA. - Further research should be carried out on the relative ecological importance of seasonally flooded grassland and deep water rice areas, particularly to the conservation of Bengal Florican. - Any further agricultural development, particularly deep water rice expansion, should not be undertaken without a full environmental impact assessment and a proper understanding, based on the above, of conversion of the semi-natural ecosystems (upon which the floricans may be reliant) to agriculture.- Current ranger patrolling and enforcement initiatives in Virachey National Park focused on illegal activities (hunting and logging) should be continued and increased to cover all important areas. - Further surveys should be carried out, particularly of the montane areas close to the borders of Lao PDR and Viet Nam, to confirm the presence or absence of globally threatened species expected to occur in this area of the southern Annamites EBA.- Measures to counter hunting and trade of wildlife must be put in place throughout the area. This should start with setting up patrolling systems in the Lomphat Wildlife Sanctuary and Mondolkiri Protected Forest. - Conservation of this important stretch of the Srepok River should be an integral part of management of the existing conservation areas. However, this must be viewed at the scale of the complete length of the river system (in conjunction with IBA #25), as focusing on just a small stretch in isolation could have disastrous consequences. - Efforts must be made to protect sandbar-nesting bird species while they are breeding. Community agreements could be set up with individual villages so that the nest areas will not be disturbed. - Immigration, illegal settlement and land encroachment into the most important and critical areas across the IBA should be prevented. - New villages and agricultural development along the Srepok River should be discouraged and key stretches of riverine forest identified should be strictly protected from logging and shifting cultivation. - A mapping of key wetlands, key species breeding areas and human presence within the IBA should be carried out. This will require further surveys, particularly in areas south of the Srepok, which remain ornithologically little known and should be used to form conservation planning. - Relevant recognition of the above in Provincial and National development plans. - Further surveys and research along the Srepok River needs to be carried out. This should focus on identifying important stretches of riverine forest, smaller backwater rivers and streams, and better determining the numbers and breeding success of sandbar-nesting species.LVALstony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P FreshwaterThis IBA comprises a contiguous area of open deciduous dipterocarp forest extending from the western parts of Lomphat Wildlife Sanctuary, to the north and west, as far as the confluence of the Sesan and Srepok Rivers. The Srepok River and its associated riverine vegetation is integral to the IBA, and both banks of the river are included within the IBA. The section of the Srepok included in the IBA is c.200 m wide, with a rocky substrate with associated shrubs. The vegetation of the IBA is dominated by , although mixed deciduous forest and, less commonly, semi-evergreen forest, also occur. Seasonal streams, often flanked by gallery forest, are found throughout the IBA, and there are numerous pools, mostly seasonal. These pools are typically less than 100 m in diameter but are often associated with large seasonal meadows, which can be several hundred metres in length. The IBA supports one of the moThis IBA comprises a contiguous area of open deciduous dipterocarp forest extending from the western parts of Lomphat Wildlife Sanctuary, to the north and west, as far as the confluence of the Sesan and Srepok Rivers. The Srepok River and its associated riverine vegetation is integral to the IBA, and both banks of the river are included within the IBA. The section of the Srepok included in the IBA is c.200 m wide, with a rocky substrate with associated shrubs. The vegetation of the IBA is dominated by , although mixed deciduous forest and, less commonly, semi-evergreen forest, also occur. Seasonal streams, often flanked by gallery forest, are found throughout the IBA, and there are numerous pools, mostly seasonal. These pools are typically less than 100 m in diameter but are often associated with large seasonal meadows, which can be several hundred metres in length. The IBA supports one of the most intact remaining examples of the bird community of the dry forests of central Indochina. The seasonal meadows are important nesting areas for Sarus Crane Grus antigone, while the pools are important for a number of large waterbirds, including Giant Ibis Pseudibis gigantea and Lesser Adjutant Leptoptilos javanicus. Also, the IBA includes Trapeang Rokar, an area of wetlands between the Srepok and Sesan Rivers, where White-shouldered Ibis Pseudibis davisoni was observed in 1998. The Srepok River supports a number of riverine species, including Masked Finfoot Heliopais personata and the recently described Mekong Wagtail Motacilla samveasnae. The relative abundance of large ungulates means that the IBA has greater potential to support viable populations of White-rumped, Long-billed and Red-headed Vultures Gyps bengalensis, G. indicus and Sarcogyps calvus than most other areas in mainland South-east Asia.@LVALB R deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper mThe IBA is located at the western edge of the Mekong Delta, and comprises an area of seasonally inundated grassland, interspersed with Melaleuca scrub, along the international border with Vietnam. The IBA is located at the northern extent of the Ha Tien plain, a once extensive area of seasonally inundated grassland and other natural habitats, which extends into Kien Giang Province, Vietnam. Large areas of natural habitat in the Vietnamese part of the Ha Tien plain have been converted into agricultThe IBA is located at the western edge of the Mekong Delta, and comprises an area of seasonally inundated grassland, interspersed with Melaleuca scrub, along the international border with Vietnam. The IBA is located at the northern extent of the Ha Tien plain, a once extensive area of seasonally inundated grassland and other natural habitats, which extends into Kien Giang Province, Vietnam. Large areas of natural habitat in the Vietnamese part of the Ha Tien plain have been converted into agriculture and aquaculture, while the mosaic of natural habitats in the Cambodian part have been reduced to around 1,000 ha in extent. The seasonally inundated grasslands support a non-breeding population of Sarus Crane Grus antigone, estimated by local people to number 80 to 150 birds. Whether these birds are part of the non-breeding population that regularly visits Kien Luong IBA (VN005) in the Vietnamese part of the Ha Tien plain is not known but, given the proximity of the two sites, this seems likely.The IBA is centred on Virachey National Park, and borders Laos to the north and Vietnam to the east. The IBA comprises all areas, primarily of evergreen and semi-evergreen forest, within and adjacent to the national park above 150 m asl. The vegetation of the IBA is dominated by dense semi-evergreen forest, interspersed with patches of true evergreen forest, upland savanna, bamboo thickets and occasional patches of mixed deciduous forest. The topography of the IBA is dominated by hills and low mountains, with most areas lying above 400 m asl, and elevations reaching over 1,500 m asl along the border with Laos. The avifauna of the IBA is quite distinct from that of lowland areas to the south and west, which are dominated by deciduous dipterocarp forest. The IBA is one of only two areas in Cambodia known to support Germain's Peacock Pheasant Polyplectron germaini, a restricted-range species. In addition, the IBA supports a number of globally threatened and near-threatened species, including Siamese Fireback Lophura diardi, Red-collared Woodpecker Picus rabieri and Great Hornbill Buceros bicornis. Virachey remains one of the most ornithologically unexplored parts of Cambodia. However, survey work in neighbouring areas of Laos and Vietnam, indicate that higher elevation areas are likely to be of particular importance for globally threatened species such as Black-hooded Laughingthrush Garrulax milleti and Black-crowned Barwing Actinodura sodangorum.LVAL \hingle and stony beaches&3The IBA comprises the Koh Rong archipelago a group of islands situated in the mouth of Kampong Saom bay, 20 km west of Sihanoukville. The largest islands are Koh Rong and Koh Rong Samlem, while smaller islands include Koh Ta and Koh Pos. The islands are characterized by sandy beaches, rocky shores, coral The IBA comprises the Koh Rong archipelago a group of islands situated in the mouth of Kampong Saom bay, 20 km west of Sihanoukville. The largest islands are Koh Rong and Koh Rong Samlem, while smaller islands include Koh Ta and Koh Pos. The islands are characterized by sandy beaches, rocky shores, coral reefs (which are often degraded), and small areas of mangrove and seagrass. The vegetation of the islands is dominated by evergreen forest, although this is degraded by logging in many places. The sandy beaches, which fringe the islands, are important breeding sites for Malaysian Plover Charadrius peronii.The IBA comprises the Koh Tang archipelago, a small group of islands situated in the Gulf of Thailand, c. 50 km south-west of Sihanoukville. The islands are situated in shallow water (up to c.50 m deep), and are characterised by small, sandy beaches, rocky shores and coral reefs. The islands all support degraded evergreen forest. The IBA supports Nicobar Pigeon Caloenas nicobarica, a species largely restricted to offshore, forested islands. In addition, Christmas Island Frigatebird Fregata andrewsi has been recorded at the IBA and potentially roosts on the satellite islands.The IBA is located within Phnom Aural Wildlife Sanctuary in the Cardamom Mountains. The IBA comprises all areas of evergreen and semi-evergreen forest above 400 m asl, which is thought to be the lower altitudinal limit of Chestnut-headed Partridge Arborophila cambodiana. The topography of the IBA is dominated by Phnom Aural, which, at around 1,813 m asl, is Cambodia's highest mountain. At elevations below 1,200 m asl, the vegetation of the IBA is dominated by lowland evergreen forest. Elevations between 1,200 and 1,500 m asl support lower montane evergreen forest, while elevations above 1,500 m asl support upper montane evergreen forest. The IBA supports both restricted-range species found in the Cambodia-Thailand-Mountains Endemic Bird Area: Chestnut-headed Partridge and Cambodian Laughingthrush Garrulax ferrarius.The IBA is located to the south of Kampong Thom town, within the inundation zone of Tonle Sap Lake. The IBA comprises and one of the largest remnant tracts of seasonally inundated grassland within the Tonle Sap floodplain, variably influenced on its eastern and northern fringes by deepwater rice. This habitat is mixed with scattered, but often extensive, areas of dense scrub, lotus swamps, sedge beds, and, in the dry season, numerous small to medium-sized ponds. At the height of the wet season (August-October), the whole IBA is inundated. Parts of the IBA lie within Tonle Sap Multiple Use Area, designated under the 1993 Royal Decree on Protected Areas, and Tonle Sap Biosphere Reserve. The IBA is a very important breeding site for Bengal Florican Houbaropsis bengalensis during the dry season (December to May). In the wet season (May to July), a number of non-breeding waterbirds visit the site, including adjutants Leptoptilos spp., Painted Stork Mycteria leucocephala and Asian Openbill Anastomus oscitans. In addition, the IBA supports a substantial wintering population of Manchurian Reed Warbler Acrocephalus tangorum, as well as small numbers of wintering Greater Spotted and Imperial Eagles Aquila clanga and A. heliaca. In addition, the largest flock of White-shouldered Ibis Pseudibis davisoni recorded in Cambodia in recent decades was observed here in 1999.LVAL33rThe IBA is situated in southern Mondulkiri and Kratie provinces, and comprises an extensive mosaic of evergreen and semi-evergreen forest habitats, from Snoul Wildlife Sanctuary in the south-west to Phnom Nam Lyr Wildlife Sanctuary in the north-east. Most of the intervening areas between the two wildlife sanctuaries are situated within a forest concession under the management of Samling International. However, this area is also managed as a biodiversity conservation area within the concession system. The vegetation of the IBA is characterised by evergreen and semi-evergreen forest on hills, grading into mixed deciduous and deciduous dipterocarp forest to the north-west. The dominant vegetation type is semi-evergreen forest, which varies greatly in structure and composition, from apparently evergreen-dominated stands with a high density of lianas, palms and rattans, to tracts with a more open understorey. Within the predominantly level lowland Snoul Wildlife Sanctuary there are numerous grassy clearings with pools within the evergreen forest. To the south-east, the IBA is contiguous with areas of natural habitat in Vietnam, a significant proportion of which is included within Bu Gia Map Nature Reserve. The results of recent surveys indicate that the IBA supports all three restricted-range species found in the Cambodia-South Vietnamese Lowlands Endemic Bird Area: Orange-necked Partridge Arborophila davidi, Germain's Peacock Pheasant Polyplectron germaini and Grey-faced Tit Babbler Macronous kelleyi. The IBA also supports a number of other globally threatened and near-threatened species, including Green Peafowl Pavo muticus, White-winged Duck Cairina scutulata, Great Hornbill Buceros bicornis and Siamese Fireback Lophura diardi. Finally, higher elevation areas within Phnom Nam Lyr Wildlife Sanctuary (up to 1,070 m asl) support some elements of a montane avifauna, which, although little studied, appears to have some similarities with that of the lower slopes of the Da Lat plateau to the east. For exampLVAL Shingle and stony beaches@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swamp<33-34P Raised and blanket bogs<33-34C Raised and blanket bogs&33-34P Desert dunes&33-34C Desert dunes:33-34P Graval and sand plains:33-34C Graval and sand plains&33-34P Stone desert&33-34C Stone desert33-34P Oases33-34C Oases&33-34P Polar desert&33-34C Polar desertD33-34P Sea cliffs and rocky shoresD33-34C Sea cliffs and rocky shores<33-34P Rock stacks and islands<33-34C Rock stacks and islandsJ33-34P Inland cliffs and rocky slopesJ33-34C Inland cliffs and rocky slopes233-34P Scree and boulders233-34C Scree and boulders33-34P Caves33-34C Caves$33-34P Arable land$33-34C Arable land&33-34P Rice paddies&33-34C Rice paddies833-34P Improved pasture land833-34C Improved pasture landV33-34P Perennial crops, orchards and grovesV33-34C Perennial crops, orchards and groves^33-34P Forestry and agro-industrial plantations^33-34C Forestry and agro-industrial plantationsN33-34P Small settlements, rural gardensN33-34C Small settlements, rural gardens$33-34P Urban areasPPPP ,u@,u@~sq_rR ReferencesBBBBBBBBBBB ,u@,u@~sq_rR IBA Site AccountNNNNNNNNNNN ,u@,u@~sq_rProtected Area Table subreportfffffffffff p۽,u@p۽,u@~sq_rPrint Report IBAJJJJJJJJJJJ ~p۽,u@p۽,u@~sq_rNew IBA report formatTTTTTTTTTTT }p۽,u@p۽,u@~sq_rLanduse Table subreportXXXXXXXXXXX |p۽,u@p۽,u@~sq_rKey Rele, these areas support Black-throated Tit Aegithalos concinnus, White-cheeked Laughingthrush Garrulax vassali and Black-chinned Yuhina Yuhina nigrimenta.LVAL[ 8)34C Moist deciduous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633- Any tourism infrastructure development in the area should not be undertaken without a full environmental impact a- Any tourism infrastructure development in the area should not be undertaken without a full environmental impact assessment and a proper understanding on the potential negative effects on the potentially fragile coastal ecosystem.- Discussions should be initiated with the relevant military authorities to control any illegal hunting and egg collecting activities on the islands.- Current ranger patrolling and enforcement initiatives in Phnom Aural Wildlife Sanctuary focused on illegal activities (hunting and logging) should be continued and increased to cover all important areas.- Law enforcement and community awareness activities should be initiated based on the successful model at Stung Sen / Santuk / Baray (IBA #21). These should focus on controlling the hunting and trade of key species, particularly Bengal Floricans and large waterbirds, and the potential benefits to local communities.- Measures to counter hunting and trade of wildlife must be put in place throughout the area. This should start with setting up patrolling systems in the Preah Vihear Protected Forest. - A mapping of key wetlands, key species breeding areas and human presence within the Preah Vihear Protected Forest should be carried out. This will require further surveys and should be used to inform conservation planning. - Relevant recognition of the above in Provincial and National development plans. - Large waterbird conservation should be incorporated into current initiatives to work with local communities to conserve Eld s Deer. - Establish community agreements on use of key wetlands, hunting dogs, egg collection and the practice of poison fishing. Investigation of possible livelihood security programs for key villages to promote such controls and secure support for site-based conservation. - Immigration, illegal settlement and land encroachment into the most important and critical areas of the Preah Vihear Protected Forest should be prevented.- The current patrolling and law enforcement initiative in the core designated Seima Biodiversity Conservation Area, focused on the hunting and trade of key species, should be expanded throughout the area. This should include ranger patrols in Phnom Nam Lyr and Snoul Wildlife Sanctuaries. Snaring, and other indiscriminate hunting practices should be strictly controlled. - Under the Ministerial Declaration for biodiversity conservation and the concession management plan, critical areas for key species in the concession should be designated as special protection areas for biodiversity conservation thereby ensuring they are not logged or disturbed. - A community awareness programme should be initiated throughout the area. This should focus on the potential to involve the indigenous Phnong communities inside the forest in conservation activities and extension of current laws to Khmer communities outside the forest. Participation should be sought for the local recognition and support of the special protection areas and the reduction in indiscriminate hunting practices. - A detailed assessment of the hunting trends and trade in the area should be carried out focusing on the role of wildlife as part of the livelihoods of local communities. Appropriate management activities should then be implemented based on this, through both community and Governmental authority structures. - In the area under concession, additional key conservation recommendations, eg the closing of non-essential roads after logging activities should be included in the Forest Management Plan. - Further focused surveys should be carried out to ascertain the status of Orange-necked Partridge in the area.:LVAL /Rhes@33-34C Shingle and stony beaches&33-34P Inland delta&33-34C Inland delta233-34P Rivers and streams233-34C Rivers and streams633-34P Riverine floodplains633-34C Riverine floodplainsB33-34P Freshwater lakes and poolsB33-34C Freshwater lakes and pools433-34P Artificial wetlands433-34C Artificial wetlands233-34P Ephemeral wetlands233-34C Ephemeral wetlands&33-34P Saline lakes&33-34C Saline lakes33-34P Saltpans33-34C Saltpans&33-34P Salt marshes&33-34C Salt marshes,33-34P Permanent swamp,33-34C Permanent swam- An assessment should be carried out of the potential of the area for the implementation of education and awareness initiatives for day visitors from Phno- An assessment should be carried out of the potential of the area for the implementation of education and awareness initiatives for day visitors from Phnom Penh. This could focus on the visiting waterbirds, especially pelicans, and could potentially be carried out in conjunction with one of the local pagodas.- Enforcement activities should be initiated as soon as possible focusing on hunting of wildlife (including egg and chick collection) and illegal fishing methods.- A local conservation program based on the successful model of Prek Toal IBA (KH003) should be initiated immediately to protect the breeding colonies of large waterbirds. - Enforcement activities should be undertaken by appropriate Government personnel to control illegal hunting and fishing activities. - Further surveys should be carried out to identify any, as yet undocumented, breeding colonies, particularly of adjutants in the dry season. - Initiate an environmental education program, based on the successful model at Prek Toal IBA (KH003). This should work with both adults and children, but particularly through the local schools.- Any development or logging in the area under its current designation as land concession should not be undertaken without a full environmental impact assessment and a proper understanding of the potential negative effects of such development on the habitats of White-shouldered Ibis. - Further surveys and research across the whole area from the Sekong River to the Lao PDR border should be undertaken in both wet and dry seasons, in order to better understand the distribution and ecology of White-shouldered Ibis. - Serious consideration should be made to giving strict protection status to key areas for White-shouldered Ibis as documented by the above surveys and research. - Immigration, illegal settlement and land encroachment into the most important and critical areas across the IBA should be discouraged.- Law enforcement and community awareness activities should be initiated based on the successful model at Stung Sen / Santuk / Baray (IBA #21). These should focus on controlling the hunting and trade of key species, particularly Bengal Floricans and large waterbirds and the potential benefits to local communities. - Further research should be carried out on the relative ecological importance of flooded grassland and deep water rice areas, particularly to the conservation of Bengal Florican. - Any further agricultural development, particularly deep water rice expansion, should not be undertaken without a full environmental impact assessment and a proper understanding, based on the above of the potential effects on the natural ecosystems upon which the Floricans are reliant. LVAL duous forest633-34P Dry deciduous forest633-34C Dry deciduous forest633-34P Dry evergreen forest633-34C Dry evergreen forest&33-34P Thorn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34C Mangroove forest@33-34P Lower montane rain forest@33-34C Lower montane rain forest@33-34P Upper montane rain forest@33-34C Upper montane rain forest833-34P Hill evergreen forest:33-34C Hill evergreen forest$33-34P Pine forest$33-34C Pine forestR33-34P Montane broadleaf evergreen forestR33-34C Montane broadleaf evergreen forestR33-34P Montane broadleaf deciduous forestR33-34C Montane broadleaf deciduous forest`33-34P Montane mixrd broadleaf-coniferous forest`33-34C Montane mixrd broadleaf-coniferous forest@33-34P Montane coniferous forest@33-34C Montane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest The IBA comprises one of the largest remnant tracts of contiguous semi-natural grassland within the Tonle Sap inundation zone. . The vegetation of the IBA is characterised by a mosaic of tall and short grass swards, mixed with some patchy, dense scrub, limited deepwater rice fields and small, scattered wetlands. Wet season rice is cultivated along the IBA s northern fringe adjacent to RN6. The seasonally inundated grassland supports the highest densities of breeding Bengal Floricans HoubaropsisThe IBA comprises one of the largest remnant tracts of contiguous semi-natural grassland within the Tonle Sap inundation zone. . The vegetation of the IBA is characterised by a mosaic of tall and short grass swards, mixed with some patchy, dense scrub, limited deepwater rice fields and small, scattered wetlands. Wet season rice is cultivated along the IBA s northern fringe adjacent to RN6. The seasonally inundated grassland supports the highest densities of breeding Bengal Floricans Houbaropsis bengalensis found in Cambodia to date, and the IBA supports a highly significant population of this species. The small pools are used as feeding areas by a number of large waterbirds dispersing from the Tonle Sap breeding colonies, including Painted Stork Mycteria leucocephala and Lesser Adjutant Leptoptilos javanicus. The IBA also supports a substantial wintering population of Manchurian Reed Warbler Acrocephalus tangorum, as well as small numbers of wintering Greater Spotted Eagle Aquila clanga.kLVAL 33-34P Riverine floodplains633-34C Riverine The IBA is situated in northern Santuk District, to the north-east of Stung Sen/Santuk/Baray IBA (KH021). The vegetation of the IBA chiefly comprises degraded deciduous dipterocarp forest, interspersed with seasonal wetlands and patches of paddy rice cultivation. The IBA is one of the only areas in Cambodia currently known to support non-breeding Bengal Floricans (Houbaropsis bengalensis), wThe IBA is situated in northern Santuk District, to the north-east of Stung Sen/Santuk/Baray IBA (KH021). The vegetation of the IBA chiefly comprises degraded deciduous dipterocarp forest, interspersed with seasonal wetlands and patches of paddy rice cultivation. The IBA is one of the only areas in Cambodia currently known to support non-breeding Bengal Floricans (Houbaropsis bengalensis), which visit the site during the wet season when their breeding areas in the inundation zone of Tonle Sap Lake are flooded. Also during the wet season, the seasonal wetlands at the IBA support a number of other globally threatened and near-threatened bird species, including Painted Stork (Mycteria leucocephala), Lesser Adjutant ( Leptoptilos javanicus) and Greater Adjutant (Leptoptilos dubius).The IBA is centred on the Stung Sen Core Area of Tonle Sap Biosphere Reserve. The IBA is located at the south-eastern end of Tonle Sap Lake, to the north of the point where the Tonle Sap River leaves the lake. The vegetation of the IBA is characterized by botanically unique gallery forest along rivers, dominated by Barringtonia acutangula and Diospyros cambodiana. Although disturbed, this habitat is the most species-rich tall forest around Tonle Sap Lake. The IBA supports an important breeding colony of Darter Anhinga melanogaster, as well as a significant breeding concentration of Grey-headed Fish Eagle (Ichthyophaga ichthyaetus).The IBA is located in the northern plains of Cambodia, and is centred on the recently decreed Forest Reserve for Conservation of Genetic Diversity, Vegetation and Wildlife Resources in Chhep and Chom Khsan districts. The vegetation of the IBA is characterised by a complex mosaic of habitats, determined by soil quality, proximity to water and topography. Poorer, sandy soils, support a variety of open deciduous dipterocarp forest types, often dominated by only a few species, that characterizes this landscape. Richer, alluvial soils, often near watercourses, support more species-rich forest, dominated by tall, mature dipterocarps, with multiple canopy layers shading a complex herbaceous understorey. Extensive grasslands and seasonal meadows form a patchwork within the open deciduous dipterocarp forest that is unique to the area, and is arguably one of the richest remaining grasslands in the whole of Asia. To the north, the IBA is contiguous with areas of similar natural habitat in Laos. The IBA supports one of the most intact remaining examples of the bird community of the dry forests of central Indochina. The IBA supports a large number of globally threatened and near-threatened bird species, including Green Peafowl Pavo muticus, White-winged Duck Cairina scutulata, Sarus Crane Grus antigone, White-rumped Vulture Gyps bengalensis, Long-billed Vulture G. indicus, Red-headed Vulture Sarcogyps calvus, Greater Adjutant Leptoptilos dubius, Lesser Adjutant Leptoptilos javanicus and Black-necked Stork Ephippiorhynchus asiaticus. Most notably, the IBA supports one of the largest remaining populations of Giant Ibis Pseudibis gigantea in the world. In addition it supports small numbers of wintering Manchurian Reed Warbler Acrocephalus tangorum.LVAL:  rn forest&33-34C Thorn forest.33-34P Mangroove forest.33-34- Law enforcement and community awareness activities should be initiated based on the successful model at Stung Sen / Santuk / Baray (IBA #21). These should focus on controlling the hunting and trade o- Law enforcement and community awareness activities should be initiated based on the successful model at Stung Sen / Santuk / Baray (IBA #21). These should focus on controlling the hunting and trade of key species, particularly Bengal Floricans and large waterbirds and the potential benefits to local communities. - The occurrence of White-shouldered Ibis in the area should be further investigated.- Current ranger patrolling and enforcement initiatives in Phnom Samkos Wildlife Sanctuary focused on illegal activities (hunting and logging) should be continued and increased to cover all important areas.- Enforcement activities should be undertaken by appropriate Government personnel to control illegal hunting and fishing activities, particularly in the Stung Sen Core Area. - The Stung Sen Core Area should be removed from the fishing lot system and give conservation status as a Fish Sanctuary under the Fisheries Law. - A local conservation program based on the successful model of Prek Toal (IBA #3) should be initiated to protect the wet season breeding colonies of Darter. - Further surveys should be carried out to identify any, as yet undocumented, breeding colonies, particularly of Darters in the wet season and adjutants in the dry season. - Initiate an environmental education program, based on the successful model in Prek Toal (IBA #3). This should work with both adults and children, but particularly through the local schools throughout the Stung Sen Core Area.- A mapping of key wetlands, breeding areas and human presence within the Phnom Prich Wildlife Sanctuary and Mondulkiri Protected Forest should be carried out. This will require further surveys and should be used to inform conservation planning. - Relevant recognition of the above in Provincial and National development plans. - Measures to counter hunting and trade of wildlife must be put in place throughout the area. This should start with setting up patrolling systems in the Phnom Prich Wildlife Sanctuary and Mondulkiri Protected Forest. - Core areas should receive strict protection under the existing structures of Phnom Prich Wildlife Sanctuary and the Mondulkiri Protected Forest. - Immigration, illegal settlement and land encroachment into the most important and critical areas across the IBA should be prevented.- A mapping of key wetlands, key species breeding areas and human presence throughout the IBA should be carried out. This will require further surveys and should be used to inform conservation planning. - Initiate a conservation planning process with the WS authorities and other relevant Provincial Government bodies based on the results of the above. Efforts should be made to ensure recognition of the above in Provincial and National development plans. - Undertake a needs analysis of the Wildlife Sanctuary and its staff in order that capacity may be strengthened appropriately and efficiently. - Current ranger patrolling and enforcement initiatives in Kulen Promtep Wildlife Sanctuary should be continued and increased to cover all important areas. Activities should focus on the control of illegal fishing methods, egg collection and the conversion or degradation of riverine habitats. - The initiative of a local conservation team to protect the Darter colony should be further supported and potentially expanded. - Immigration, illegal settlement and land encroachment into the Kulen Promtep Wildlife Sanctuary should be prevented, particularly involving planned resettlement of former military personnel.1LVALL Eciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P RiThe IBA comprises Boeung Veal Samnap, a permanent lake located to the east of Phnom Penh. The areas surrounding the lake become inundated when the Mekong River floods during the wet season, and thus support extensive marshes, bordered by rice cultivation. The vegetation of the marshes comprises various grasses and sedges, while other emergent spThe IBA comprises Boeung Veal Samnap, a permanent lake located to the east of Phnom Penh. The areas surrounding the lake become inundated when the Mekong River floods during the wet season, and thus support extensive marshes, bordered by rice cultivation. The vegetation of the marshes comprises various grasses and sedges, while other emergent species and rafts of floating vegetation cover extensive areas of the lake, there are also small areas of swamp forest trees. A number of large waterbirds regularly occur at the IBA in the wet season, including small numbers of Spot-billed Pelican (Pelecanus philippensis). In 2000 a colony of Darter (Anhinga melanogaster) was discovered in the IBA.The IBA is situated on the western shore of Tonle Sap Lake, to the south of Prek Toal IBA (KH003). The vegetation of the IBA comprises of flooded swamp forest and dense shrubland with emergent large trees, such as Xanthophyllum glaucum, Terminalia cambodiana and Barringtonia acutangula. The IBA is situated within the Tonle Sap Multiple Use Area, designated under the 1993 Royal Decree on Protected Areas, and the Tonle Sap Biosphere Reserve. The IBA supports breeding colonies of Darter (Anhinga melanogaster), Lesser Adjutant (Leptoptilos javanicus) and Greater Adjutants (L. dubius).The IBA comprises of an area of open deciduous dipterocarp forest in western Siem Pang District, which is bordered to the east by the Sekong River, and to the north and west by Xe Pian Protected Area in Laos. The topography of the IBA is dominated by a flat plain, which rises in the extreme north, close to the international border with Laos, to form a series of low hills. The vegetation of the IBA is dominated by deciduous dipterocarp forest, which is relatively open in places and denser in others, and has a grassy understorey. Scattered throughout the forest are a number of pools and seasonally wet meadows. The western bank of the Sekong River supports a strip of tall gallery forest, while the hills in the north of the IBA support semi-evergreen forest. Along the western bank of the Sekong River, in the area to the west of Siem Pang town, and along the road between Siem Pang town and Road No. 13, areas of forest have been converted into agricultural land, much of which is only cultivated during the rainy season. The IBAsupports the most significant population of the globally critical White-shouldered Ibis Pseudibis davisoni yet known in Cambodia. This species has been observed at a number of wetlands on the flat plain, close to Siem Pang town, and is reported to breed in the west of the district, close to the international border with Laos. The IBA also supports a range of other globally threatened and near-threatened bird species, characteristic of the dry forests of central Indochina, including vultures, Green Peafowl (Pavo muticus), Sarus Crane (Grus antigone), Giant Ibis (Pseudibis gigantea), Lesser Adjutant (Leptoptilos javanicus) and Asian Golden Weaver (Ploceus hypoxanthus).Z X  q eaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest steppe(33-34C Forest steppe(33-34P Forest tundra(33-34C Forest tundra@33-34P Temperate heath and scrub@33-34C Temperate heath and scrub033-34P Semi-desert scrub033-34C Semi-desert scrubB33-34P Subalpine and alpine scrubB33-34C Subalpine and alpine scru(.U@C ;h**FSeng Kim Hout and Pech BunnatKHStung / Prasat BalangStung / Prasat BalangCambodiaKampong Thom ProvinceStung, Prasat Balang and Kampong Svay DistrictsANE@|Biome12A1?@aA1 & A3:@{t]]Y:҆(-T@ R 5#g/^ Seng Kim Hout and Pech BunnatKHCentral CardamomsCentral CardamomsCambodiaPursat, Kompong Speu & Koh Kong ProvincesKravanh District ; Aural District ; Veal Veng & Thmar Baing DistrictsANEy@|SA85Biome09A1L@aA1 & A2@]@ca@ `K@{i]QQE90$$ p]]Y:(,Q@&\ i Seng Kim Hout and Pech BunnatKHBassac MarshBassac MarshCambodiaKandal ProvinceKean Svay, Saang, Leuk Dek & Koh Thom DistrictsANE@|A1A4iA4i = Whiskered TernA1 & A4i@F     yk]]Y:(+Q@5 h(Seng Kim Hout and Pech BunnatKHChhnuk TruChhnuk TruCambodiaPursat & Kampong Chhnang ProvincesKrakor District ; Baribo DistrictANE(@zA1A4iA4i=2000 Whiskered TernsA1 & A4i@c@{)ui]]Y:()O@ $7 :,j,lSeng Kim Hout and Pech BunnatKHTonle SekongSekong RiverCambodiaStung Treng ProvinceSiem Pang, Sesan & Stung Treng DistrictsANE@zA1A2-Mekong WagtailA1 & A2W@]]@cH@{% yk]]Y:(&I@$ 'h1* Seng Kim Hout and Pech BunnatKHBasset MarshBasset MarshCambodiaKandal Province & Phnom Penh CityPonhealou & Ang Snuol Districts ; Dangkao DistrictANE_@zA1A19@tyk]]Y:(%I@%, $"iSeng Kim Hout and Pech BunnatKHBoeung Veal SamnapBoeung Veal SamnapCambodiaKandal ProvinceLvea Em & Khsach Kandal DistrictsANE@xA1A4iA4i = Oriental DarterA1 & A4i@t     q]]Y:($I@S 1g4Seng Kim Hout and Pech BunnatKHDei RoneatDei RoneatCambodiaPursat ProvinceBakan DistrictANEN@xA1A4iA4i - Greater AdjutantA1 & A4i_@]@c@t ui]]Y:(#I@ j7Seng Kim Hout and Pech BunnatKHWestern Siem PangWestern Siem PangCambodiaStung Treng ProvinceSiem Pang DistrictANE@xBiome11A1A4iA4i-Giant IbisA1, A3 & A4iW@]H@ `4@t)p]]Y:fLVAL z Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P ConiferousThe IBA comprises Chhnuk Tru, an inland delta formed where the Tonle Sap and Stung Sen Rivers meet the Tonle Sap Lake. During the dry season, the IBA contains large areas of exposed mudflat, bisected by a complex of small, medium and large waterways. During the dry season (March to May), the IBA is important for large numbers of migratory shorebirds, although more survey work needs to be carried outThe IBA comprises Chhnuk Tru, an inland delta formed where the Tonle Sap and Stung Sen Rivers meet the Tonle Sap Lake. During the dry season, the IBA contains large areas of exposed mudflat, bisected by a complex of small, medium and large waterways. During the dry season (March to May), the IBA is important for large numbers of migratory shorebirds, although more survey work needs to be carried out to establish the patterns of use of the IBA by migratory shorebirds and feeding large waterbirds from the colonies to the northwest. The area also regularly supports more than 1% of the Asian biogeographic population of Whiskered Tern Chlidonias hybridus. The IBA is situated within Tonle Sap Multiple Use Area, designated under the 1993 Royal Decree on Protected Areas, and Tonle Sap Biosphere Reserve.The IBA comprises the stretch of the Sekong River from the international border with Laos to its confluence with Mekong River. Along this stretch of the river, there are many different habitats, many of which can be catagorised as channel mosaics of rock and sand islands with riverine scrub. There are no stretches dominated by extensive sandbars, and significant stretches are slow-moving and relatively featureless. For much of its length, the Sekong River is fringed by a belt of gallery forest, about 100 m wide, which is significantly taller than the adjacent deciduous dipterocarp forest, and contains a high proportion of broadleaf evergreen trees. However this has been degraded or cleared for cultivation in many areas. The IBA supports a suite of bird species restricted to wide, lowland rivers, including River Lapwing Vanellus duvaucelii, Small Pratincole Glareola lactea, Great Thick-knee Esacus recurvirostris and River Tern Sterna aurantia. In addition, the IBA supports Mekong Wagtail Motacilla samveasnae, a recently described species, which is thought to be endemic to the Mekong River and its major tributaries. Furthermore, at certain times of the year, the IBA may be important for a number of large waterbirds, including Giant Ibis Pseudibis gigantea.The IBA comprises of Basset Marsh, a permanent lake located along Road No. 5, about 12 km north of Phnom Penh. The areas surrounding the lake become inundated when the Tonle Sap River floods during the wet season, and thus support extensive marshes. These marshes are surrounded by agricultural land, mainly riceSmall numbers of Spot-billed Pelicans Pelecanus philippensis are regular in the wet season and Darters Anhinga melanogaster are also regular. The IBA is the only known site thus far in Cambodia where River Tern Sterna aurantia has been recorded away from the upper Mekong in the wet season. Grey-headed Fish Eagle Icthyophaga ichthyaetus has also been recorded once and is probably no more than an irregular visitor. Due to its proximity to Phnom Penh and easy access, the IBA has great potential for conservation awareness and education programmes.LVAL  restB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest steppe(33-34C Forest steppe(33-34P Forest tundra(33-34C Forest tundra@33-34P Temperate heath and scrub@33-34C Temperate heath and scrub033-34P Semi-desert scrub033-34C Semi-desert scrubB33-34P Subalpine and alpine scrubB33-34C Subalpine and alpine scrub,33-34P Secondary scrub,33-34C Secondary scrub.33-34P Wooded grassland.33-34C Wooded grassland33-34P Tundra33-34C Tundra33-34P Steppe33-34C Steppe033-34P Edaphic grassland033-34C Edaphic grasslandJ33-34P Alpine and subalpine grasslandJ33-34C Alpine and subalpine grassland433-34P Secondary grassland433-34C Secondary grasslandd33-34P Shallow marine waters, corel reefs and keysd33-34C Shallow marine waters, corel reefs and keys"33-34P Sea inlet- Law enforcement and community awareness activities should be initiated based on the successful model at Stung Sen/Santuk/Baray IBA (KH021). These should - Law enforcement and community awareness activities should be initiated based on the successful model at Stung Sen/Santuk/Baray IBA (KH021). These should focus on controlling the hunting and trade of key species, particularly Bengal Floricans and large waterbirds and the potential benefits to local communities- Law enforcement on the crackdown of wildlife hunting, trade and illegal logging should be strengthened in the whole Cardamom Mountains. - Any development in the area without biodiversity impact assessment is to be prohibited or stopped - Land encroachment and forest clearance for agricultural purposes should be discouraged- Further surveys should be undertaken in the low water season from April to July to better understand the importance of the area for feeding waterbirds, both post-breeding large waterbirds from the Tonle Sap and migratory shorebirds. - Enforcement activities should be undertaken by appropriate Government officers focusing on controlling hunting and disturbance of waterbirds and illegal fishing methods.- Efforts must be made to protect sandbar-nesting bird species while they are breeding. Community agreements could be set up with individual villages so that the nest areas will not be disturbed. - Conservation of the Sekong River should be at the scale of the complete length of the river system, as focusing on just a small stretch in isolation could have disastrous consequences. - New villages and agricultural development along the river should be discouraged and key stretches of riverine forest identified should be strictly protected from logging and shifting cultivation. - Further surveys and research need to be carried out. These should focus on identifying important stretches of riverine forest, smaller backwater rivers and streams, and better determining the numbers and breeding success of sandbar-nesting species.LVAL& ntane coniferous forestB33-34P Broadleaf deciduous forestB33-34C Broadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Coniferous forest033-34C Coniferous forest.33-34P Riverline forest.33-34C Riverline forest(33-34P Forest steppe(33-34C Forest steppe(33-34P Forest tundra(33-34C Forest tundra@33-34P The IBA is located to the north-east of Stung/Chi Kreng/Kampong Svay Grasslands IBA (KH016), and comprises an area of deciduous dipterocarp forest, interspersed with patches of seasonally inundated grassland, seasonal pools and streams. The IBA is one of the only currently known non-breeding areas for Bengal Florican Houbaropsis bengalensis in Cambodia. The speciesThe IBA is located to the north-east of Stung/Chi Kreng/Kampong Svay Grasslands IBA (KH016), and comprises an area of deciduous dipterocarp forest, interspersed with patches of seasonally inundated grassland, seasonal pools and streams. The IBA is one of the only currently known non-breeding areas for Bengal Florican Houbaropsis bengalensis in Cambodia. The species visits the site when its breeding areas in the inundation zone of Tonle Sap Lake are flooded. In addition, the wetland habitats at the IBA are used as a feeding area by a number of large waterbird species, including Painted Stork Mycteria leucocephala, Woolly-necked Stork Ciconia episcopus, Asian Openbill Anastomus oscitans and Lesser Adjutant Leptoptilos javanicus.The IBA is located in the Cardamom Mountains, between Phnom Samkos (KH012) and Phnom Aural IBAs (KH014). The IBA comprises all areas of evergreen and semi-evergreen forest in the central Cardamom Mountains above 400 m asl, which is thought to be the lower altitudinal limit of Chestnut-headed Partridge Arborophila cambodiana. The topography of the IBA is mountainous, although maximum elevations are lower than within the adjacent IBAs. The vegetation of the IBA is dominated by lowland evergreen forest, with hill evergreen forest above 1,000 m asl. The IBA supports Chestnut-headed Partridge one of the two restricted-range species found in the Cambodia-Thailand Mountains Endemic Bird Area. Furthermore, the large expanses of relatively intact lowland evergreen forest within the IBA make it a potentially important site for the conservation of Great Hornbill Buceros bicornis. Historically both White-winged Duck Cairina scutulata and White-shouldered Ibis Pseudibis davisoni were recorded along rivers within the IBA in 1944, but their current status is unknown. Most of the IBA is included within the Central Cardamoms Protected Forest.The IBA comprises an extensive area of wetlands between the Mekong and Bassac Rivers. The vegetation of the IBA is dominated by seasonally inundated shrub and savanna swamp, which is surrounded by agricultural land. During the wet season, the IBA is inundated, and is characterised by large areas of deep, open water, with substantial areas of emergent, floating and submerged aquatic vegetation. The IBA supports large numbers of commoner waterbirds, as well as small numbers of Darter Anhinga melanogaster, Spot-billed Pelican Pelecanus philippensis and Asian Golden Weaver Ploceus hypoxanthus. In addition, the IBA regularly supports more than 1% of the Asian biogeographic population of Whiskered Tern (Chlidonias hybridus). Z @ @ @ @ @________ _ _  llllllllll IIIIIIII I!I "I #y$y%y&y)y+y,y-y.y34C Semi-desert scrubB33-34P Subalpine and alpine scrubB33-34C Subalpine and alpine scrub,33-34P Secondary scrub,33-34C Secondary scrub.33-34P Wooded grassland.33-34C Wooded grassland33-34P Tundra33-34C Tundra33-34P Steppe33-34C Steppe033-34P Edaphic grassland033-34C Edaphic grasslandJ33-34P Alpine and subalpine grasslandJ33-34C Alpine and subalpine grassland433-34P Secondary grassland433-34C Secondary grasslandd33-34P Shallow marine waters, corel reefs and keysd33-34C Shallow marine waters, corel reefs and keys"33-34P Sea inlets"33-34C Sea inlets33-34P Open sea33-34C Open sea*33-34P Estuary waters*33-34C Estuary watersN33-34P Internal mud, sand or salt flatsreportXXXXXXXXXXX ڕ,u@ڕ,u@~sq_rSpecies TableDDDDDDDDDDD W,u@ڕ,u@~sq_rR threats<<<<<<<<<<< W,u@W,u@~sq_rR SpeciesAreaCompilerTTTTTTTTTTT W,u@W,u@~sq_rR Species NoteFFFFFFFFFFF W,u@W,u@~sq_rR Species at IAB SitesVVVVVVVVVVV ,u@,u@~sq_rR Site decriptionLLLLLLLLLLL ,u@,u@~sq_rR Site AccountFFFFFFFFFFF ,u@,u@~sq_rR Secondary SpeciesPPPPPPPPPPP ,u@,u@~sq_rR ReferencesBBBBBBBBBBB ,u@,u@~sq_rR IBA Site AccountNNNNNNNNNNN ,u@,u@~sq_rProtected Area Table subreportfffffffffff p۽,u@p۽,u@~sq_rPrint Report IBAJJJJJJJJJJJ ~p۽,u@p۽,u@~sq_rNew IBA report formatTTTTTTTTTTT }p۽,u@p۽,u@~sq_rLanduse Table subreportXXXXXXXXXXX |p۽,u@p۽,u@~sq_rKey Reference Table subreportddddddddddd {p۽,u@p۽,u@~sq_rIntervention Table subreportbbbbbbbbbbb zp۽,u@p۽,u@~sq_rIBA Data Form QueryPPPPPPPPPPP OoEX. L " z P & b D & p ( k eG)_5 m5 oa`6 qGZ04C ciB@ gci\@ gci\@ gci\@ gci\@ gci\@ gci \@ gci D@ gci BA Data Form].[11 Area]8 gci h@ gci f@ gci[IBA Data Form].[8 Country]: gciV@ gciL@ gciD@ gciL@ gci[IBA Data Form].[2 Date]7 gci[IBA Data Form].[1 Compiler]; gci![IBA Data Form].[Serial number]> gciIBA Data Form+++ ci Gci Gci ci GciIBA Data FormSpecies Tablej@QE+ ciB@ gci[Species Table].[23 Species]; gcif@ gciL@ gciSpecies Table+++ ciIBA Data Form+++ ci ci GciB@  gciV@  gciL@  gciD@  gciL@  giciIBA Data Form+++ iciT Recommendation111 ci Gci Gici ci GIBA Data FormProtected Area Tablex@_S+ IBA Data FormSpecies Tablej@QE+ Z@ g[Species Table].[Census year]< g [Species Table].[26 Abundance]= g[Species Table].[23 Species]; gProtected Area Table999 Species Table+++ IBA Data Form+++   G L@ '@ '5[IBA Data Form].[59 Notes]9 g4`@ g3P@ g2Z@ g1L@ g0P@,! g/P@+! g.F@*! g-P@)! g,[IBA Data Form].[50 Notes]9 g+[IBA Data Form].[49 Overlap]; g*P@(! g)\@'! g(\@&! g'\@%! g&\@$! g%\@#! g$\@"! g#BA Data Form].[46 Area]8 g"D@!! g!"[IBA Data Form].[44 Designation]? g BA Data Form].[43 Year]8 gLVAL,Z  N l : F  N hVB.bv*P Tadleaf deciduous forestP33-34P Mixed broadleaf-coniferous forestP33-34C Mixed broadleaf-coniferous forest033-34P Conife[IBA Data Form].[47 Central Coordinates Lat 2][IBA Data Form].[47 Central Coordinates Lat 1][IBA Data Form].[45 IUCN category][IBA Data Form].[42 Full Name of Site][IBA Data Form].[41 Political Units][IBA Data Form].[22 Criteria Notes][IBA Data Form].[21 Criteria Proposed][IBA Data Form].[20 Biome Code Proposed][IBA Data Form].[19 EBA Code Proposed][IBA Data Form].[18 General Description][IBA Data Form].[16 Management Plan][IBA Data Form].[14 Altitude Max][IBA Data Form].[14 Altitude Min][IBA Data Form].[13 Central Coordinates Lon 3][IBA Data Form].[13 Central Coordinates Lon 2][IBA Data Form].[13 Central Coordinates Lon 1][IBA Data Form].[13 Central Coordinates Lat 3][IBA Data Form].[13 Central Coordinates Lat 2][IBA Data Form].[13 Central Coordinates Lat 1][IBA Data Form].[12 Area Accuracy][IBA Data Form].[10 Administrative Region (Level 2)][IBA Data Form].[9 Administrative Region (Level 1)][IBA Data Form].[7 International Site Name][IBA Data Form].[6 National Site Name][IBA Data Form].[5 Final IBA Code][IBA Data Form].[4 Temporary IBA Code][IBA Data Form].[Serial number] =[Species Table].[ID][Species Table].[23 English Name][IBA Data Form].[9 Administrative Region (Level 1)][IBA Data Form].[6 National Site Name][T Recommendation].Recommendation[IBA Data Form].[7 International Site Name][IBA Data Form].[6 National Site Name][IBA Data Form].[5 Final IBA Code][IBA Data Form].[4 Temporary IBA Code][IBA Data Form].[Serial number] =[Protected Area Table].[ID][IBA Data Form].[Serial number] =[Species Table].[ID][Protected Area Table].[42 Full Name of Site][IBA Data Form].[4 Temporary IBA Code]((([IBA Data Form].[4 Temporary IBA Code]) Between [First Data Form] And [Last Data Form])