Kamyshovoe-Zhamankol Lakes (22516)
Kazakhstan, Central Asia
Site overview
KBA status: confirmed
Global KBA criteria: A1b, A1d, D1a
Year of last assessment: 2006
National site name: Kamyshovoe-Zhamankol Lakes
Central coordinates: Latitude: 53.9583, Longitude: 65.9167
System: freshwater, terrestrial
Elevation (m): 162 to 180
Area of KBA (km2): 39.39646
KBA classification: Global
Legacy site: Yes
Site details
Site description: This group of lakes lies in the Kostanai Plain at the northern point of the Ubagan-Ishym Interfluve. The majority of the group is in the frontier area of Uzynkol district of Kostanai Region. Only the southern quarter of Zhamankol lake lies in the adjacent Sarykol district. The lakes are situated 7 km to the south-east of Korolyovka and 37 km to the north-west of the district centre of Uzynkol. The regional centre of Kostanai lies 200 km to the north-east. The lakes are the permanent standing freshwater bodies with two major sources of refilling: seasonal floods and freshets, and the groundwater upwelling. A perennial variation in the volume of meltwaters results in an unstable hydrological regime though there is a pattern of rather regular cycles. The wetlands have vigorous reed growth, both mosaics and solid patches. The surrounding landscape which formerly consisted of herb-rich feather-grass steppe with small stands of Aspen-Birch forest, has almost completely be transformed to agriculture and nowadays consists of an assortment of crop-fields. As the lakes appear to receive a regular supply of groundwater, compared to the majority of waterbodies of the dry-steppe sub-zone they remain largely unaffected by the drastic fluctuations of precipitation. A few parts of the plain around the lakes have retained patches of the original grass-herb vegetation consisting of Stipa zalesskii, Festuca valesiaсa, Salvia stepposa, Phlomis agrarian and Galatella divaricata. During the second half of the 1990s a substantial portion of the arable land was neglected and has turned, with time, into 'wasteland' with an exuberant growth of ruderal weeds (Artemisia absinthium, Sonchus arvensis, Taraxacum officinale, Convolvulus arvensis, Turritis glabra and Nonnea pulla). However, since 2000 there has been a tendency towards agricultural reclamation of these abandoned plots. The lakes are set in distinct hollows and have stable margins that often form low cliffs 1.5-2 m in height. The waters of Kamyshovoye (Lebyazh’ye) Lake cover an area of 4.7 km2 with a fringing belt of reed and cat-tail 100-150 m in width. Nearer the shore, this solid growth gives way to patches of reed interspersed with Scolochloa festucacea, Sonchus arvensis and Saussurea amara. Marshy areas have Carex disticha, C. acutiformis and C. omskiana. Further away from the water there is a narrow belt of moist meadows with a patchwork of grasses including Juncus gerardii, Alopecurus pratensis, Phalaroides arundinaceae, Calamagrostis epigeios and Elytrigia repens. The pattern of aquatic vegetation is directly linked to the particular state of the lakes flooding: when water levels are low there is additional reed growth dividing the waters into a series of vast open stretches that support seasonal concentrations of waterbirds. In addition to stands of Typha angustifolia and Scirpus lacustris in the shallows, the open water often has a rich growth of carpet-forming water-plants (Alisma plantago-aquatica, Butomus umbellatus, Myriophyllum verticilatum, Potamogeton lucens, P. perfoliatus and Ceratophyllum demersum). Sampling has established the presence of 53 species of algae. The gently sloping banks of the littoral form muddy margins that attract considerable numbers of gulls and waders. Along the edge of the bank terraces there is low scrub (Rosa cinnamomea) with patches of steppe vegetation (Salvia stepposa, Serratula cardunculus). In a very few spots there are patches of the almost extinct grassland type - Stipa korshinskyi dominated steppe-grass associations historically growing on rich calcareous soils. Lake Zhamankol is 2.6 x 2.2 km, and its shoreline stretches for 11.4 km. The waters are half covered with extensive reedbeds forming quagmires in several places. In general, the banks have reeds interspersed with patches of Scirpus lacustris and Juncus gerardii, with reed mixed with Carex disticha and C. acutiformes in some places. Beyond the shore there are meadows with a predominance of Alopecurus pratensis and Phalaroides arundinaceae, and further away dry meadows comprised mostly of Poa pratensis and Leymus ramosus. Along the margin of the top terrace there are fragments of the well-preserved original Festuca-Artemisia Steppe. Beyond this the area has been almost entirely converted to agriculture with many fields which following harvest are feeding areas for migrating waterfowl. Part of the abandoned arable land has developed a dense scrub of bushy Artemisia which is perfect habitat for the local population of Roe deer. Within a short distance of the shores there are a few groves of deciduous forest (Aspen and Birch). A characteristic feature of the regional climate are frequent and strong winds.
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: The site provides plentiful opportunities for large numbers of waterbirds to breed, moult and concentrate when on passage. More than 50 species of waterbirds have been recorded, including Gaviiformes – 1, Podicipediformes – 4, Pelecaniformes – 1, Ciconiformes – 3, Anseriformes – 19, Rallidae – 2, Charadriformes – 12, Laridae – 8 and Gruiformes – 2. Based on observations from May 1998 and 1999 and June 2004, the majority of the breeding fauna consists of dabbling ducks (69.6%), diving ducks (13.4%), gulls (4%), waders (2.8%), swans (2.5%) and grebes (1.4%). Greylag Goose also nests. The dominant species was Anas penelope (57.5 %), plus Aythya ferina (12.7 %), Anas acuta (5.4 %), Anas strepera (3.4 %), Cygnus cygnus (2.5 %), Anas querquedula (2.2 %), Larus ridibundus (1.7%), Vanellus vanellus (1.0 %), Limosa limosa (1.2 %)and Podiceps cristatus (1.0 %). Species occurring infrequently include Podiceps griseigena, Egretta alba, Ardea cinerea, Botaurus stellaris, Fulica atra, Grus grus, Grus virgo, Anser anser, Anas platyrhynchos, Anas crecca, Anas clypeata, Aythya ferina, Aythya fuligula, Larus cachinnans, L. ridibundus, L. canus, L. minutus, Sterna hirundo, Chlidonias niger, Chl. leucoptera and Glareola nordmanni. On passage there are remarkable concentrations of Greylag and White-fronted Geese; at the peak of the migration period flocks of 50,000 birds are common. The site also often has good numbers of Branta ruficollis and Anser erythropus. In recent years there have been occasional autumn records of Chen hyperboreus. Other species in autumn concentrations of birds include Anas platyrhynchos (50%), A. acuta (23%), Fulica atra (7.1%), A. strepera, A. penelope, Podiceps cristatus, P.nigricollis, Larus cachinnans, L. ridibundus, L. canus and Cygnus cygnus. Species occurring in smaller numbers include Pluvialis squatarola, Calidris alpina, Phalocrocorax carbo, Anas crecca and Casmerodius albus. Kamyshonoye lake is well known for its regular moulting concentrations of Cygnus cygnus, C. olor (150-200 birds) and Anser anser (200-300 individuals). The avifauna of the adjacent land also exhibits significant diversity, including woodland species because of the presence of small forest stands. Ten species included in the Red Data Book of Kazakhstan occur: breeding - Cygnus cygnus and Grus grus; passage - Grus grus, Anser erythropus, Branta ruficollis and Aythya nyroca. Rare raptors include Haliaeetus albicilla, Aquila heliaca and Falco peregrinus. Falco vespertinus nests in the neighboring field-protecting forest belts, Circus macrourus and Glareola nordmannii in the lakes’ hollows. Aquila clanga and Cygnus columbianus occur occasionally. Non-bird biodiversity: The fish population of Kamyshovoye lake contains only 2 species - Carassius carassius and Carassius auratus - and Zhamankol also has Perca fluviatilis. Amphibians and reptiles are represented by Bufo viridis, Rana arvalis and Lacerta agilis. Mammals include 25 species: Capreolus pygargus, Alces alces (passage), Meles meles, Mustela eversmanni, Mustela erminea, Mustela nivalis, Vulpes corsac, Vulpes vulpes, Canis lupus, Lepus timidus and Lepus europaeus. The most numerous are rodents. Damp areas are occupied by Microtus arvalis, Microtus oeconomus, Arvicola terrestris and Ondatra zibetica; while the steppe biotopes hold large numbers of Cricetus cricetus, Lagurus lagurus, Ellobius talpinus and Spermophilus erythrogenus. A few groups of Marmota bobac remain in the region around Kamyshovoye lake. In former times the steppe area adjacent to the lakes consisted of widespread patches of motley herbs and turf-grasses within the extensive swathes of Stipa korshinskyi. Now all areas have been transformed into arable land and the fragments of these unique steppe associations can only be seen along the margins of Kamyshovoye lake.
Habitats
Summary of habitats in KBA: The lakes are used as a traditional fishery: the waters of Zhamankol have 1-2 teams of fishermen using stationary nets, a technique which is potentially dangerous as birds frequently get trapped by such devices. As practically all of the area around the lakes is cultivated, the only places remaining acceptable for grazing are the narrow belts of meadows lying within the inner margin of lakes’ hollows. This, and the gradually reviving cattle-raising industry, means that the lush vegetation of the meadows is being severely affected. In the early 1990s the local agrarian industry suffered a recession and fell into a bad state which has begun to recover since 1999. From 2000 to 2005 the majority of cultivated land has been reclaimed. As this region provides almost perfect natural conditions for wheat growing, it is likely that there will be continuing agricultural intensification. The lakes are reckoned to be one of the best game areas of the region for waterfowl hunting.
Land use: agriculture (16%) | fisheries/aquaculture (40%) | hunting (50%) | rangeland/pastureland (30%)
| IUCN Habitat | Coverage % | Habitat detail |
|---|---|---|
| Wetlands(Inland) | 51 | |
| Grassland | 32 | |
| Artificial - Terrestrial | 16 | |
| Shrubland | 1 |
Threats
Summary of threats to biodiversity at KBA: Presently, apart from the fluctuating water supply, the most serious pressures on the ecosystems of the lakes are the small-scale fishery, hunting and agro-industrial activities. The site is situated in an area that has been subject to an almost continuous agricultural boom for many years and cultivation is closing in on the lakes on all sides, halting its encroachment just short of the lush fringing vegetation belt. The relative intensification of agriculture in recent years threatens the purity of the water through accidental drainage of fertilizers and pesticides. There is also considerable disturbance from the intensive use of harvesting or cultivating machinery and a nearby network of country roads. Intensive goose hunting also causes disturbance. Thus the major negative factors affecting the site are: the impact on the lush vegetation zone by mowing or cattle-grazing activities; the threat of water pollution by pesticide run-off; disturbance from large-scale fishing and hunting (with frequent poaching). Trampling of the shore vegetation, essential bird breeding habitat (including that of Glareola nordmanni), has been alleviated to a certain extent on account of a sharp decline in the number of local livestock in the mid 1990s. However, this pressure is beginning to return.
| Threat level 1 | Threat level 2 | Threat level 3 | Timing |
|---|---|---|---|
| Biological resource use | Hunting & collecting terrestrial animals | Intentional use (species being assessed is the target) | Ongoing |
| Biological resource use | Hunting & collecting terrestrial animals | Unintentional effects (species being assessed is not the target) | Ongoing |
| Natural system modifications | Fire & fire suppression | Increase in fire frequency/intensity | Ongoing |
| Agriculture & aquaculture | Annual & perennial non-timber crops | Small-holder farming | Ongoing |
| Human intrusions & disturbance | Work & other activities | Ongoing |
Additional information
References: Berezovikov N.N. (2002) Kamyshovoye-Zhamankol group of lakes. The most important wetlands of Northern Kazakhstan (in limits of Kostanay and west part of North-Kazakhstan regions). Edited by Bragin E.A. and BraginaT.M.- Moscow: Russian University (series WWF, issue 5): P.65-69. (in Russian) Bragin E.A., and BraginaT.M. (2002) T.M. Wetlands in system of natural complexes of Northern Kazakhstan. General characteristic and nature-protection importance. The most important wetlands of Northern Kazakhstan (in limits of Kostanay and west part of North-Kazakhstan regions). Edited by Bragin E.A. and BraginaT.M.- Moscow: Russian University (series WWF, issue 5): 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) Bragin E.A. (2005) The results of the field expedition run for the Project “Slender-billed Curlew”: Kostanai Region// Kazakhstan Ornithological Bulletin, 2004. Almaty: “Tethys” publishing, P. 43-45. (in Russian) Gvozdetsky N.A., Nikolayev V.A. (1971) Kazakhstan. – Moscow, Publ.House “Mysl’”, 294 p. (in Russian) Yerokhov S.N. (1997) Contemporary fauna of Water-birds of Kostnai Region. Evaluation of game-species resources (Preliminary report)// Kostnai, 1997. (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.121-157. (in Russian) Yerokhov S.N., Berezovikov N.N. (2003) Monitoring of Waterfowl and Shore-bird species on the lakes of Kostanai Region (Norther Kazakhstan) in October of 2001 and 2002. Russia Ornithological Journal, Express-issue, 228: P.744-749. (in Russian) Yerokhov S.N., Berezovikov N.N.(2004) Ornithological observations in Kostanai Region in the autumn of 2003// Kazakhstan Ornithological Bulletin, 2004. Almaty: “Tethys” publishing, P. 46-48. (in Russian) Yerokhov S.N., Kellomyaki E.N., Karpov F.F., Vilkov V.S. (2006) Monitoring of autumn migration of water-birds and appraisal of their intrinsic habitats’ condition in Kostanai Region in 2005// Kazakhstan Ornithological Bulletin, 2005. Almaty: “Tethys” publishing,. P.41-45. (in Russian) Filonets O.O., Omarov A.A. (1974) Lakes of Northern, Western and Eastern Kazakhstan. Reference-book, ”HydroMetIzdat” Publ. House, L. (in Russian) J.Markkola, P.Pynnonen, P.Tolvanen, A.Veersaly & S.Yerohov. (1998) The second International Lesser White-fronted Geese Anser erythropus expedition in NW Kazakhstan in May 1997. WWF. Finland Report # 9. Finnish Lesser White-fronted Goose Conservation Project. Annual report, 1997. Helsinki, p. 21- 22. P.Tolvanen & P.Pynnonen. (1998) Monitoring the autumn migration of Lesser White-fronted Geese Anser erythropus and other gees in NW Kazakhstan in October 1996. WWF. Finland Report # 9. Finnish Lesser White-fronted Goose Conservation Project. Annual report, 1997. Helsinki, p. 19- 20. P.Tolvanen, T. Aarvak & T. Bragina (2001) Conservation work for the wetlands and monitoring the autumn staging of Lesser White-fronted Geese in the Kustanay region, north-west Kazakhstan, in 2000. WWF. Finland Report # 13. Fennoscandian Lesser White-fronted Goose Conservation Project. Annual report, 2001. Helsinki, p. 30- 33.