Shoshkaly Lake System (22003)
Kazakhstan, Central Asia
Site overview
KBA status: confirmed
Global KBA criteria: A1d
Year of last assessment: 2007
National site name: Shoshkaly Lake System
Central coordinates: Latitude: 53.6667, Longitude: 64.9333
System: freshwater, terrestrial
Elevation (m): 92 to 103
Area of KBA (km2): 135.71389
KBA classification: Global
Legacy site: Yes
Site details
Site description: The lake system lies on the right bank of the flood valley in the middle reaches of the Ubagan river. It is located 10 km to the south of Karatal village, 45 km to the south-west of the district centre of Uzunkol and 155 km north-east of Kostanai. Until the mid 1980s the Shoshkaly Lake System represented a typical steppe zone, reed covered cluster of flood-plain lakes. However, following an increase in the level of the Ubagan river due to dam construction in its lower reaches, the system has been transformed into a single, large waterbody occupying an area of 3,000 ha. The surrounding landscape is a flat or gently undulated alluvial plain. The system is fed, almost exclusively, by spring melt-waters via run-off from the vast expanse of the Turgay rift valley and flooding by the Ubagan river. At present, the lake is 9.5 x 4 km in size and consists of a patchwork of reedbeds separated by substantial stretches of open water. Although lying in a region that has been traditionally used for wheat production, the salinity of the soil surrounding the lake has meant that it has not be cultivated - the closest fields are 10-15 km away. About 10-12 km to the east, where the Turgay valley begins to rise, there are woodland blocks of birch and aspen.
Rationale for qualifying as KBA: This site qualifies as a Key Biodiversity Area of international significance that meets the thresholds for at least one criterion described in the Global Standard for the Identification of KBAs.
Additional biodiversity: 57 species have been recorded, the main breeding species being Fulica atra, Podiceps cristatus, P. griseigena, P. nigricolis, Anser anser, Anas platyrhynchos, A. strepera, A. penelope, A. acuta, A. crecca, A. querquedula, Aythya ferina, Netta rufina, Aythya fuligula, Cygnus olor, Egretta alba, Ardea cinerea, Phalocrocorax carbo (at the end of the 1990s there was a colony of about 1,000 individuals), Pelecanus onocrotalus, P. crispus, Larus ridibundus, L. canus, L. argentatus, Sterna hirundo, Chlidonias leucoptera, Numenius arquata, Limosa limosa, Vanellus vanellus and Glareola nordmanni. At the beginning of August 1998 dabbling duck numbers reached 40,000 birds. At the beginning of June 2000 numbers were in the region of 25-30,000, predominantly ducks but also large numbers of Anser anser (8 broods per every linear kilometre of surveyed shoreline). Moulting birds include large numbers of swans and diving ducks and northern breeding waders. During migration waterbird numbers reach 50-80,000 birds. At the end of September 1997, it was estimated that there were 1,295 birds per square kilometre, with the dominant species being Anas platyrhynchos (38%), A. acuta (18.1%) and Fulica atra (14.3%). Melanocorypha leucoptera breeds in small numbers on the saline areas of the adjacent steppe. Rare and endangered species breeding at the site include Pelecanus onocrotalus and P. crispus (250-300 breeding pairs in 2000), small numbers of Grus grus and Oxyura leucocephala, and Grus virgo and Tetrax tetrax on the steppe. Vanellus gregarius was found in August 1998. The environs of the lake are the feeding ground of a pair of Haliaeetus albicilla nesting in the nearby deciduous groves. Circus macrourus also breeds. On passage Aquila clanga is recorded occasionally. Migrating flocks of Branta ruficollis, Anser erythropus and Cygnus cygnus are not infrequent, with more rarely, Cygnus columbianus. In September 1998 there was a record of two Chen hyberboreus. Non-bird biodiversity: About 30 species of mammal occur around the lake: Alces alces (straggler), Capreolus pygargus (common - 50 in February 1999), Sus scrofa (formerly resident but now only visiting groups), Canis lupus (8 observed in the winter of 1998-1999), Vulpes vulpes (common), Vulpes corsac (rare), Nyctereutes procyonoides (rare), Mustela eversmanni, Mustela erminea, Mustela nivalis, Meles meles, Marmota bobac, Lepus europaeus, Spermophillus erythrogenus (common), Ondatra zibetica (common), Arvicola terrestris (abundant), Microtus oeconomus, Microtus arvalis and Lagurus lagurus. The ichthyofauna comprises 8 species, of which three - Tinca tinca, Carassius carassius and Carassius auratus - had commercially viable populations. Common waterplants are Potamogeton sp., Ceratophyllum demersum and Myriophyllum spicatum. There are scattered stands of Salix sp. and Elaeagnus. The alkali areas support Halimione verrucifera and Artemisia nitrosa, while a prominent part of the meadow vegetation consists of Juncus gerardii, Leymus angustrus and Leymus ramosus. The elevated drier areas have Festuca valesiaca, Artemisia nitrosa, Spiraea hypericifolia and Artemisia procera. Damp depressions are overgrown with Stipa capillata. The area of the watershed consists of mixture of Stipa zalesskii, Stipa capillata and Galatella villosa.
Habitats
Summary of habitats in KBA: Because of a profusion of alkaline land in the Ubagan river valley, the terrestrial parts of the Shoshkaly lake system were not converted to agricultural land which has impacted on most of the flood valley and neighboring plains. Cattle raising was formerly well-developed but underwent a major decline in the early 1990s, and continues to decline today. The major part of the steppe extending from the eastern shore of the lake is used for winter grazing of local horses. During the period of 1998-2006 there was negligible fishing on the lake. In autumn the surroundings of the lake are turned into hunting grounds, with the licensed shooting of gamebirds, musk-rat and, irregularly, roe deer. There are no permanent settlements on the lake, the nearest being 12 and 16 km away.
Land use: fisheries/aquaculture | hunting (100%) | rangeland/pastureland (10%)
| IUCN Habitat | Coverage % | Habitat detail |
|---|---|---|
| Artificial - Aquatic | 1 | |
| Grassland | 54 | |
| Wetlands(Inland) | 45 |
Threats
Summary of threats to biodiversity at KBA: It is expected that the area will face a dramatic increase in fishing activities and a growing demand for grazing in the coming years, especially along the eastern shore. Recent artificial changes in the water regime threatens the integrity of the bank system, including erosion of the dam. Flooding of new areas and steppe fires can also have a negative effect on bird populations.
| Threat level 1 | Threat level 2 | Threat level 3 | Timing |
|---|---|---|---|
| Agriculture & aquaculture | Livestock farming & ranching | Small-holder grazing, ranching or farming | Ongoing |
| Agriculture & aquaculture | Livestock farming & ranching | Agro-industry grazing, ranching or farming | Ongoing |
| Biological resource use | Fishing & harvesting aquatic resources | Unintentional effects: large scale (species being assessed is not the target) [harvest] | Ongoing |
| Natural system modifications | Dams & water management/use | Dams (size unknown) | Ongoing |
| Natural system modifications | Fire & fire suppression | Increase in fire frequency/intensity | Ongoing |
| Biological resource use | Hunting & collecting terrestrial animals | Intentional use (species being assessed is the target) | Only in the future |
| Biological resource use | Fishing & harvesting aquatic resources | Unintentional effects: large scale (species being assessed is not the target) [harvest] | Only in the future |
Additional information
References: Berezovikov N.N. (2002) Shoshkaly lake system. The most important wetlands of Northern Kazakhstan (in limits of Kostanay and west part of North-Kazakhstan regions). Bragin, E.A. and Bragina T.M, eds. Moscow, Russian University Press P. 90-94. (in Russian). Bragin, E.A. and Bragina T.M. (2002). Wetlands in system of nature complexes of Northern Kazakhstan. General characteristic and nature conservation importance. Bragin, E.A. and Bragina T.M, eds. The most important wetlands of Northern Kazakhstan (in limits of Kostanay and west part of North-Kazakhstan regions). Moscow, Russian University Press (WWF series, issue 5): P. 19-38. (in Russian). Bragin E.A. (2004). Distribution and population numbers of swans in Kostanai Region in 1998-2002. Transactions of Institute of Zoology, V. 47. “Migrations of birds in Asia”, Almaty. P. 75-86. (in Russian). Yerokhov S.N. (1999). Preliminary results of the monitoring of geese autumn migration taking its course through the territory of Kostanai Region (Northern Kazakhstan). The problems of protection and sustainable use of biodiversity of wildlife of Kazakhstan.( Materials of international scientific conference of the 6-8 of April 1999) Almaty: P. 64-65. (in Russian). Yerokhov S.N., Berezovikov N.N., Kellomyaki E.N., Ripatti N.L. (2000). Anser erythropus and concomitant species of geese on their migration in Kazakhstan. Brant # 6, Bulletin of the working group on geese and swans of Eastern Europe and Central Asia., M.,P.121-1 Yerokhov S.N., Berezovikov N.N.(2003). Monitoring of water-fowl and shore-bird species at the Lakes of Kostanai Region (Northern Kazakhstan) in October of 2001 and 2002. Russian Ornithological Journal. Express Issue 228: P.744-749. Bragin E.A., Bragina T.M. (2000) Dynamics level of the lakes and population of Birds and Mammals in Kustanay Region. Biodiversity and Dynamics of Ecosystems in North Eurasia. BDENE. Volume 3. Diversity of the Fauna of North Eurasia. Part 2. Novosibirsk, Russia. August 21- 26, 2000. IC&G. Novosibirsk. PP. 229- 231.