
TOP > 生物多様性センターの国際協力 > ESABII > Database > Migrant Birds Database > Temminck's Stint
Common Name | Temminck's StintBirdlife International | |||||||||||||||||||||||||||||||||||||||||||||
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Species name | Calidris temminckiiBirdlife International | |||||||||||||||||||||||||||||||||||||||||||||
Family | Scolopacidae | |||||||||||||||||||||||||||||||||||||||||||||
Genus | ||||||||||||||||||||||||||||||||||||||||||||||
Local Name |
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No descriptions
No descriptions
This species is a full migrant, migrating on a broad front1 overland across the full width of Europe, North Africa and the Middle East2. Adults leave their young in July before they are fully fledged and migrate south to the wintering grounds2; juveniles then leave the breeding grounds in early-August2. Some individuals also winter in Europe as far north as Britain1. The species arrives in the wintering grounds in Africa from late-July to October, and departs for the return migration in late-March to April1, breeding between late-May and early-July on returning to the breeding range1. The species feeds singly or in groups of up to 30 individuals1 and migrates singly or in small parties, although between 100 and 250 individuals have been encountered at some European staging sites2.
<Breeding> This species breeds in arctic tundra, shrub tundra and forest tundra along flood-plains1, although it avoids extremely cold conditions and exposed coasts2. It is mainly found near coastal inlets, fjords, deltas, rivers or streams from sea level to 250 m, but also occurs up to 1,200 m inland2 on flat, clear ground with little vegetation, areas covered with short grass and interspersed with patches of scrub1, areas with grasses, sedges or Empetrum, and scrub willow or birch thickets with sandy or gravelly stretches4. Both dry and wet areas are used, but habitats with elevated locations such as boulders or buildings are preferred because of their use as song perches4. In Scandinavia the species also breeds near fishing huts and houses, and in industrial workings7.
<Non-breeding> Outside of the breeding season the species inhabits inland freshwater wetlands such as flood-lands, irrigated fields, sewage farms, densely vegetated wetlands1, 2, ditches, muddy marshes and lake edges3, and on the coast shows a strong preference for mudflats in sheltered inlets, estuaries and saltmarshes, whilst tending to avoid open and sandy beaches2.
On the breeding grounds and in inland habitats the diet of this species consists primarily of insects and their larvae (especially beetles and Diptera such as craneflies and midges)1, 4, as well as the occasional plant matter1. On the coasts the species takes annelids, crustaceans1 (such as sand fleas)4 and small molluscs1.
The nest is a shallow cup2 on the ground in the open or amongst low vegetation1, 2, often at the base of small willows, junipers or other shrubs4.
1. del Hoyo et al. (1996). 2. Snow and Perrins (1998). 3. Urban et al. (1986). 4. Johnsgard (1981). 5. Koivula and Ronka (1998). 6. Ronka et al. (2006). 7. Ronka (1996). 8. Melville and Shortridge (2006).
LC
This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence <20,000 km2 combined with a declining or fluctuating range size, habitat extent/quality, or population size and a small number of locations or severe fragmentation). The population trend is not known, but the population is not believed to be decreasing sufficiently rapidly to approach the thresholds under the population trend criterion (>30% decline over ten years or three generations). The population size is very large, and hence does not approach the thresholds for Vulnerable under the population size criterion (<10,000 mature individuals with a continuing decline estimated to be >10% in ten years or three generations, or with a specified population structure). For these reasons the species is evaluated as Least Concern.
<Trend justification> The population trend is difficult to determine because of uncertainty over the extent of threats to the species.
Country | Category | Reference |
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Brunei Darussalam | ||
Cambodia | ||
China | ||
Indonesia | ||
Japan | ||
Korea | ||
Lao PDR | ||
Malaysia | ||
Mongolia | ||
Myanmar | ||
Philippines | ||
Singapore | ||
Thailand | ||
Vietnam |
This species is threatened by nest predation5, 6 from Common Gull Larus canus and Ruddy Turnstone Arenaria interpres6, as well as from Hooded Crow Corvus corone cornix, weasel Mustela nivalis, American mink Mustela vison and fox Vulpes vulpes in Finland7. It is also threatened in its Scandinavian breeding range by shrinkage and deterioration of suitable habitats (due to eutrophication and the overgrazing of shore meadows), and by increased human recreational disturbance due to the building up of breeding sites (trampling and disturbance often lead to increased hatchling predation and abandonment of nests)7. The species is also susceptible to avian influenza and may therefore be threatened by future outbreaks of the virus8.
No descriptions
No descriptions
No descriptions
Country | Status | Reference |
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Brunei Darussalam | ||
Cambodia | ||
China | ||
Indonesia | ||
Japan | ||
Korea | ||
Lao PDR | ||
Malaysia | Protected Wild Birds Part I: Game Birds(as Calidris temmincki) | Law of Malaysia Act 76, Protection of Wild Life Act 1972 (Amend. 2006) |
Mongolia | ||
Myanmar | ||
Philippines | ||
Singapore | ||
Thailand | ||
Vietnam |
The Asian Waterbird Census (AWC) was initiated in 1987 and runs in parallel with other waterbird censuses carried out in Africa, Europe, Central and West Asia and Latin America under the umbrella of the International Waterbird Census (IWC), which is organised by Wetlands International.
The AWC takes place annually, during the second and third weeks of January, and is carried out by volunteers interested in collecting information on waterbirds and wetlands as a basis for contributing to their conservation.
Reference: Li, Z.W.D., Bloem, A., Delany S., Martakis G. and Quintero J. O. 2009. Status of Waterbirds in Asia - Results of the Asian Waterbird Census: 1987-2007. Wetlands International, Kuala Lumpur, Malaysia
BRUNEI DARUSSALAM | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
The number of observed individual | 1 | 1 | ||||||||||||||||||||
The number of observed sites(not all count sites) | 1 | 1 | ||||||||||||||||||||
The total number of count sites | 2 | 3 | 3 | 2 | 4 | 4 | 0 | 4 | 4 | 4 | 4 | 5 | 5 | 0 | 0 | 0 | 9 | 0 | 0 | 1 | 0 | 9 |
CAMBODIA | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | ||||||||||||||||||||||
The number of observed sites(not all count sites) | ||||||||||||||||||||||
The total number of count sites | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 0 | 11 | 0 | 0 | 12 | 12 | 11 | 5 | 1 | 6 | 9 | 6 | 6 |
CHINA | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | 8 | 21 | 15 | 10 | 8 | 1 | 42 | |||||||||||||||
The number of observed sites(not all count sites) | 1 | 1 | 1 | 1 | 2 | 1 | 2 | |||||||||||||||
The total number of count sites | 0 | 1 | 34 | 12 | 50 | 60 | 67 | 29 | 6 | 14 | 6 | 15 | 21 | 20 | 14 | 10 | 22 | 45 | 80 | 81 | 59 | 72 |
INDONESIA | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | 6 | 20 | ||||||||||||||||||||
The number of observed sites(not all count sites) | 1 | 1 | ||||||||||||||||||||
The total number of count sites | 0 | 0 | 0 | 1 | 19 | 8 | 17 | 17 | 15 | 19 | 16 | 0 | 0 | 47 | 12 | 10 | 40 | 34 | 14 | 16 | 15 | 23 |
JAPAN | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | 18 | 20 | 28 | 28 | 24 | 6 | 9 | 5 | ||||||||||||||
The number of observed sites(not all count sites) | 8 | 9 | 8 | 8 | 5 | 2 | 3 | 2 | ||||||||||||||
The total number of count sites | 0 | 0 | 0 | 53 | 39 | 52 | 47 | 20 | 50 | 40 | 47 | 37 | 41 | 37 | 107 | 112 | 103 | 109 | 97 | 159 | 142 | 137 |
LAO PDR | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | ||||||||||||||||||||||
The number of observed sites(not all count sites) | ||||||||||||||||||||||
The total number of count sites | 0 | 0 | 0 | 2 | 4 | 5 | 3 | 2 | 1 | 0 | 0 | 0 | 0 | 0 | 14 | 1 | 0 | 0 | 0 | 1 | 0 | 0 |
MALAYSIA | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | 300 | 1 | 237 | 1 | ||||||||||||||||||
The number of observed sites(not all count sites) | 1 | 1 | 2 | 1 | ||||||||||||||||||
The total number of count sites | 0 | 0 | 0 | 59 | 68 | 93 | 85 | 17 | 10 | 7 | 10 | 0 | 0 | 20 | 25 | 25 | 25 | 43 | 43 | 82 | 82 | 40 |
MYANMAR | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | 6 | 56 | 87 | 74 | 36 | 91 | 21 | 142 | ||||||||||||||
The number of observed sites(not all count sites) | 1 | 4 | 5 | 5 | 3 | 3 | 2 | 4 | ||||||||||||||
The total number of count sites | 0 | 5 | 3 | 12 | 17 | 15 | 21 | 20 | 13 | 12 | 2 | 4 | 2 | 0 | 7 | 32 | 47 | 73 | 24 | 31 | 32 | 19 |
PHILIPPINES | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | ||||||||||||||||||||||
The number of observed sites(not all count sites) | ||||||||||||||||||||||
The total number of count sites | 0 | 0 | 0 | 0 | 19 | 21 | 34 | 39 | 46 | 47 | 39 | 28 | 29 | 32 | 43 | 38 | 50 | 47 | 56 | 54 | 65 | 108 |
SINGAPORE | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | ||||||||||||||||||||||
The number of observed sites(not all count sites) | ||||||||||||||||||||||
The total number of count sites | 0 | 0 | 0 | 0 | 4 | 12 | 17 | 15 | 13 | 14 | 10 | 10 | 6 | 11 | 10 | 10 | 8 | 9 | 9 | 8 | 8 | 7 |
REPUBLIC OF KOREA | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | ||||||||||||||||||||||
The number of observed sites(not all count sites) | ||||||||||||||||||||||
The total number of count sites | 0 | 0 | 10 | 12 | 22 | 20 | 20 | 15 | 10 | 22 | 25 | 22 | 14 | 68 | 99 | 112 | 118 | 116 | 117 | 123 | 127 | 127 |
THAILAND | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | 16 | 352 | 37 | 35 | 6 | 2 | 9 | 38 | 25 | 4 | 2 | 70 | 112 | 132 | 143 | 179 | ||||||
The number of observed sites(not all count sites) | 4 | 6 | 4 | 2 | 1 | 1 | 3 | 3 | 2 | 1 | 1 | 3 | 6 | 10 | 8 | 9 | ||||||
The total number of count sites | 10 | 8 | 3 | 20 | 26 | 12 | 23 | 16 | 17 | 5 | 9 | 3 | 1 | 1 | 7 | 3 | 9 | 26 | 20 | 82 | 99 | 33 |
VIETNAM | 1986 | 1987 | 1988 | 1989 | 1990 | 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 |
The number of observed individual | 38 | 2 | ||||||||||||||||||||
The number of observed sites(not all count sites) | 1 | 1 | ||||||||||||||||||||
The total number of count sites | 0 | 0 | 0 | 1 | 2 | 0 | 1 | 4 | 0 | 1 | 1 | 0 | 1 | 8 | 2 | 2 | 16 | 4 | 4 | 9 | 6 | 11 |