| Location | Cambodia |
| Central coordinates | 103o 19.00' East 13o 51.00' North |
| IBA criteria | A1, A3, A4i, A4iii |
| Area | 12,659 ha |
| Altitude | 14 - 27m |
| Year of IBA assessment | 2003 |
Ornithological information 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.
Site description 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.
| Species | Season | Period | Population estimate | Quality of estimate | IBA Criteria | IUCN Category |
|---|---|---|---|---|---|---|
| Lesser Whistling-duck Dendrocygna javanica | unknown | 1998 | abundant [units unknown] | - | A4i | Least Concern |
| Comb Duck Sarkidiornis melanotos | unknown | 1998 | abundant [units unknown] | - | A4i | Least Concern |
| Milky Stork Mycteria cinerea | non-breeding | 1998 | rare [units unknown] | - | A1 | Vulnerable |
| Asian Openbill Anastomus oscitans | non-breeding | 1998 | abundant [units unknown] | - | A4i | Least Concern |
| Black-necked Stork Ephippiorhynchus asiaticus | non-breeding | 1998 | rare [units unknown] | - | A4i | Near Threatened |
| Lesser Adjutant Leptoptilos javanicus | unknown | 1998 | common [units unknown] | - | A1 | Vulnerable |
| Greater Adjutant Leptoptilos dubius | unknown | 1998 | unknown [units unknown] | - | A1 | Endangered |
| Black-headed Ibis Threskiornis melanocephalus | non-breeding | 1998 | unknown [units unknown] | - | A4i | Near Threatened |
| White-shouldered Ibis Pseudibis davisoni | unknown | 1998 | rare [units unknown] | - | A1 | Critically Endangered |
| Spot-billed Pelican Pelecanus philippensis | non-breeding | 1998 | abundant [units unknown] | - | A1, A4i | Near Threatened |
| Rufous-winged Buzzard Butastur liventer | unknown | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| Greater Spotted Eagle Aquila clanga | unknown | 1998 | unknown [units unknown] | - | A1 | Vulnerable |
| Eastern Imperial Eagle Aquila heliaca | unknown | 1998 | rare [units unknown] | - | A1 | Vulnerable |
| Bengal Florican Houbaropsis bengalensis | unknown | 1998 | unknown [units unknown] | - | A1, A3 | Critically Endangered |
| Sarus Crane Grus antigone | non-breeding | 1998 | abundant [units unknown] | - | A1, A4i | Vulnerable |
| Green-eared Barbet Megalaima faiostricta | unknown | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| Blue-winged Pitta Pitta moluccensis | unknown | 1998 | uncommon [units unknown] | - | A3 | Least Concern |
| Common Woodshrike Tephrodornis pondicerianus | unknown | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| Brown-rumped Minivet Pericrocotus cantonensis | unknown | 1998 | uncommon [units unknown] | - | A3 | Least Concern |
| Burmese Shrike Lanius collurioides | unknown | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| Racket-tailed Treepie Crypsirina temia | unknown | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| Indochinese Bushlark Mirafra erythrocephala | resident | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| Streak-eared Bulbul Pycnonotus blanfordi | unknown | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| White-shouldered Starling Sturnus sinensis | unknown | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| Black-collared Starling Sturnus nigricollis | unknown | 1998 | unknown [units unknown] | - | A3 | Least Concern |
| Plain-backed Sparrow Passer flaveolus | resident | 1998 | common [units unknown] | - | A3 | Least Concern |
| A4iii Species group - waterbirds | unknown | 2004 | 20,000 individuals | unknown | A4iii |
| Protected area | Designation | Area (ha) | Relationship with IBA | Overlap with IBA (ha) | |
|---|---|---|---|---|---|
| Ang Trapeng Thmor | Protected Forest | 12,906 | protected area contained by site | 10,250 |
|
| IUCN habitat | Habitat detail | Extent (% of site) |
|---|---|---|
| Artificial landscapes (aquatic) | minor | |
| Forest | Moist deciduous forest (tropical) | minor |
| Artificial landscapes (terrestrial) | Rice paddies | 50% |
| Wetlands (inland) | Artificial wetlands | minor |
| Land-use | Extent (% of site) |
|---|---|
| other | - |
| agriculture | - |
| nature conservation and research | - |
Other biodiversity 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.[Long-tailed Macaque (Macaca fascicularis)]Malayan Box Turtle (Cuora ambionensis), Malayan Snail-eating Turtle (Malayemys subtrijuga), Elongated Tortoise (Indotestudo elongata).Eld's Deer (Cervus eldii)
Management considerations 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.
Protection status Ang Tropeang Thmor Sarus Crane Conservation Area
Conservation response Recommendations: 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.
Further web sources of information
References Document nameGoes, F. and Hong Chamnan (2001). Ang Trapeang Thmor Sarus Crane Conservation Area, a major site for bird conservation in North-west Cambodia. Wildlife Conservation Society, Phnom Penh.
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Recommended citation BirdLife International (2013) Important Bird Areas factsheet: Ang Tropeang Thmor. Downloaded from http://www.birdlife.org on 25/05/2013
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