
TOP > 生物多様性センターの国際協力 > ESABII > Database > Migrant Birds Database > Whimbrel
Common Name | WhimbrelBirdlife International | |||||||||||||||||||||||||||||||||||||||||||||
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Species name | Numenius phaeopusBirdlife International | |||||||||||||||||||||||||||||||||||||||||||||
Family | Scolopacidae | |||||||||||||||||||||||||||||||||||||||||||||
Genus | ||||||||||||||||||||||||||||||||||||||||||||||
Local Name |
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No descriptions
No descriptions
This species is fully migratory and travels over land on a broad front utilising few staging areas on route (in autumn no known concentrated staging occurs)1, 5. It breeds from May to August2 either in well-dispersed3 solitary pairs1 or in loose groups depending on the topography of the land5. The autumn migration occurs from July onwards2 with the return passage to the breeding grounds occurring chiefly between March and May2 (non-breeders may also remain on the wintering grounds all year round)1. When not breeding the species usually forages singly or in small groups1, flying in small parties3 or larger flocks on migration4, 5 and roosting communally at night in mangrove trees or in shallow water1.
<Breeding> The species breeds on dry scrub heathland5, moss and lichen tundra with stunted bushes3, sedge meadows3, wet moorland1, 5 and mossy hummock bogs4, 3 in open areas, river valleys1, along the shores of tundra lakes4, in birch forest near the Arctic treeline1, burned areas of forest4 and open montane forest1 in the boreal, subarctic and subalpine zones1, 3. It generally avoids extremes of cold and wet, steep slopes, bare rock and gravel expanses or tall dense vegetation (e.g. dense forest)5.
<Non-breeding> On passage in the autumn and spring the species frequents wetlands, tidal flats1, short-sward wet and dry grasslands1, 2, farmland2 and heathland with Empetrum spp., generally occupying coastal habitats in the winter such as muddy, rocky or sandy beaches1, coral shores6, exposed reefs, tidal mudflats1, sandflats6, mangrove swamps1, tidal marshes3 and lagoons6.
When inland on migration and during the breeding season its diet consists of adult and larval insects1, 3 (e.g. Coleoptera, Orthoptera and cranefly larvae), spiders, millipedes, earthworms, snails, slugs, seeds, leaves and berries1 (e.g. of ericaceous plants)3. On the coast during the winter the species takes crustaceans (e.g. crabs), molluscs, large polychaete worms and occasionally fish, reptiles or young birds1.
The nest is a shallow depression1, 5 often positioned on hummocks or in short heather or grass3, 4 in dry exposed locations1, 3, 4 sometimes far from water3, 4. When the breeding habitat (e.g. tundra or heathland) is flat and open the species nests in solitary pairs, but where irregular features such as hummocks and tall vegetation patches give more visual isolation the species may nest in loose groups5.
1. del Hoyo et al. (1996). 2. Hayman et al. (1986). 3. Johnsgard (1981). 4. Flint et al. (1984). 5. Snow and Perrins (1998). 6. Urban et al. (1986). 7. Melville and Shortridge (2006). 8. Grant (1992). 9. Grant et al. (1992).
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). Despite the fact that the population trend appears to be decreasing, the decline is not believed to be sufficiently rapid to approach the thresholds for Vulnerable under the population trend criterion (>30% decline over ten years or three generations). The population size is extremely 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 overall population trend is decreasing, although some populations may be stable and others have unknown trends (Wetlands International 2006). This species has undergone a large and statistically significant decrease over the last 40 years in North America (-84.7% decline over 40 years, equating to a -37.5% decline per decade; data from Breeding Bird Survey and/or Christmas Bird Count: Butcher and Niven 2007) Note, however, that these surveys cover less than 50% of the species's range in North America.
Country | Category | Reference |
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Brunei Darussalam | ||
Cambodia | ||
China | ||
Indonesia | ||
Japan | ||
Korea | ||
Lao PDR | ||
Malaysia | ||
Mongolia | ||
Myanmar | ||
Philippines | ||
Singapore | ||
Thailand | ||
Vietnam |
The species is susceptible to avian influenza so may be threatened by future outbreaks of the virus7.
A study in the Shetland Islands, UK found that when trying to enhance the grazing quality of heathlands by re-seeding (e.g. with high quality grass-seed mixtures) it is better to apply lime, grass-seed and inorganic fertiliser directly to the surface of the ground rather than ploughing and harrowing the ground first, as the latter maintains more natural vegetation hummocks and heather used by the species for nesting8. Re-seeding of heathland with prior ploughing and harrowing may improve feeding conditions for pre-breeding adults however9.
No descriptions
No descriptions
Country | Status | Reference |
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Brunei Darussalam | ||
Cambodia | ||
China | ||
Indonesia | Protected Species | Goverment Regulation no. 7 / 1999, about Preservation of Plants and Animals |
Japan | ||
Korea | ||
Lao PDR | ||
Malaysia | Protected Wild Birds Part I: Game Birds | 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 |
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The number of observed individual | 8 | |||||||||||||||||||||
The number of observed sites(not all count sites) | 2 | |||||||||||||||||||||
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 | 172 | |||||||||||||||||||||
The number of observed sites(not all count sites) | 3 | |||||||||||||||||||||
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 | 17 | 1 | 62 | 3 | 1 | |||||||||||||||||
The number of observed sites(not all count sites) | 2 | 1 | 1 | 1 | 1 | |||||||||||||||||
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 | 750 | 553 | 59 | 191 | 1282 | 887 | 92 | 114 | 149 | 50 | 111 | 1 | 137 | 52 | 808 | |||||||
The number of observed sites(not all count sites) | 1 | 8 | 3 | 5 | 9 | 10 | 2 | 5 | 5 | 1 | 3 | 1 | 9 | 2 | 5 | |||||||
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 | 3 | 3 | 8 | 25 | 3 | 71 | 68 | 64 | 42 | 28 | 49 | 27 | 65 | |||||||||
The number of observed sites(not all count sites) | 1 | 1 | 2 | 2 | 1 | 9 | 10 | 10 | 9 | 5 | 5 | 5 | 6 | |||||||||
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 | 384 | 2132 | 1048 | 1322 | 1247 | 2022 | 212 | 13 | 944 | 693 | 928 | 577 | 1649 | 881 | 2459 | 4900 | 1666 | |||||
The number of observed sites(not all count sites) | 9 | 14 | 18 | 18 | 4 | 3 | 4 | 1 | 6 | 8 | 6 | 6 | 11 | 9 | 32 | 34 | 13 | |||||
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 | 2 | 21 | 25 | 7 | 436 | 6 | 2 | 20 | 116 | 1218 | ||||||||||||
The number of observed sites(not all count sites) | 1 | 2 | 1 | 2 | 1 | 1 | 1 | 1 | 3 | 11 | ||||||||||||
The total number of count sites | 0 | 5 | 3 | 12 | 17 | 15 | 19 | 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 | 467 | 210 | 700 | 318 | 153 | 669 | 117 | 290 | 153 | 165 | 610 | 463 | 565 | 428 | 769 | 183 | 153 | 613 | ||||
The number of observed sites(not all count sites) | 9 | 10 | 21 | 16 | 18 | 17 | 8 | 10 | 13 | 12 | 21 | 16 | 18 | 15 | 14 | 14 | 13 | 29 | ||||
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 | 69 | 88 | 247 | 315 | 224 | 341 | 217 | 329 | 149 | 321 | 71 | 112 | 261 | 240 | 107 | 267 | 480 | 437 | ||||
The number of observed sites(not all count sites) | 2 | 5 | 6 | 7 | 7 | 9 | 9 | 4 | 5 | 6 | 5 | 4 | 6 | 5 | 5 | 1 | 3 | 3 | ||||
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 | 504 | 2 | 21 | 40 | 93 | 39 | 28 | 409 | 192 | 65 | 60 | 19 | 289 | 728 | 261 | |||||||
The number of observed sites(not all count sites) | 4 | 1 | 2 | 1 | 3 | 3 | 2 | 2 | 1 | 1 | 4 | 2 | 5 | 11 | 6 | |||||||
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 | 4 | 6 | 11 | 60 | ||||||||||||||||||
The number of observed sites(not all count sites) | 1 | 1 | 1 | 2 | ||||||||||||||||||
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 |