Revision of the East Asian-Australasian Flyway (EAAF) Population Estimates for 37 listed Migratory Shorebird Species (Hansen et al. prepared for the Department of the Environment, 2016)
- Revision of the East Asian-Australasian Flyway Population Estimates for 37 listed Migratory Shorebird Species (PDF – 4.45 MB)
- Revision of the East Asian-Australasian Flyway Population Estimates for 37 listed Migratory Shorebird Species (DOC – 29.77 MB)
Migratory shorebirds present a particular conservation challenge because their patterns of movement take them across multiple international boundaries, in some cases almost spanning the globe. They utilise different sites in different countries at different times of the year, and conservation of these species therefore requires the management of the suite of sites that are important to them. To identify important habitat in Australia count data and population estimates are required.
Under the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act), ‘important habitat’ is a key concept for migratory species, as identified in EPBC Act Policy Statement 1.1 Significant Impact Guidelines – Matters of National Environmental Significance 2009. Defining this term for migratory shorebirds in Australia is important to ensure that habitat necessary for the ongoing survival of the 37 species is appropriately managed.
Important habitats in Australia for migratory shorebirds under the EPBC Act include those recognised as nationally or internationally important. The widely accepted and applied approach to identifying internationally important shorebird habitat throughout the world has been through the use of criteria adopted under the Ramsar Convention.
According to this approach, wetland habitat should be considered internationally important if it regularly supports:
- 1 per cent of the individuals in a population of one species or subspecies of waterbird or
- a total abundance of at least 20,000 waterbirds.
Nationally important habitat for migratory shorebirds can be defined using a similar approach to these international criteria, i.e. if it regularly supports:
- 0.1 per cent of the flyway population of a single species of migratory shorebird or
- 2,000 migratory shorebirds or
- 15 migratory shorebird species.
To determine population thresholds needed to identify important habitat, the Department previously used population estimates published in the Bamford et al., (2008) report. However, given these published figures are now almost 10 years old, they required updating.
The revised flyway population estimates use newly available data and different analytical approaches to those used in previous population estimate assessments. As a result, the numbers reported cannot be compared with previous estimates to draw conclusions about population trends. Dedicated analyses on data that are comparable over time are the only way to make conclusions about population trends. Any differences between the report’s figures and previous estimates reflect an increase in knowledge and information about migratory shorebirds in the EAAF over the past decade. They do not necessarily represent actual increases or decreases in population size and cannot be used to infer trends in this manner.
Latham’s Snipe (Gallinago hardwickii)*
Latham’s Snipe does not commonly aggregate in large flocks or use the same habitats as many other migratory shorebird species. Consequently, habitat important to Latham’s Snipe is not regularly identified using the process outlined above and different criteria are therefore necessary. Threshold criteria are still considered the best way to identify important sites in the absence of data sufficient for more rigorous methods. Important habitat for Latham’s Snipe is described as areas that have previously been identified as internationally important for the species, or areas that support at least 18 individuals of the species.
A summary of the revised population estimates for 37 migratory shorebirds.
| Common Name | Flyway population estimate | 1% Flyway Population | 0.1% Flyway Population |
|---|---|---|---|
| Asian Dowitcher | 14,000 | 140 | 14 |
| Bar-tailed Godwit | 325,000 | 3250 | 325 |
| Black-tailed Godwit | 160,000 | 1600 | 160 |
| Broad-billed Sandpiper | 30,000 | 300 | 30 |
| Common Greenshank | 110,000 | 1100 | 110 |
| Common Redshank | 75,000-150,000 | 750 | 75 |
| Common Sandpiper | 190,000 | 1900 | 190 |
| Curlew Sandpiper | 90,000 | 900 | 90 |
| Double-banded Plover | 19,000 | 190 | 19 |
| Far Eastern Curlew | 35,000 | 350 | 35 |
| Great Knot | 425,000 | 4250 | 425 |
| Greater Sand Plover | 200,000-300,000 | 2000 | 200 |
| Grey Plover | 80,000 | 800 | 80 |
| Grey-tailed Tattler | 70,000 | 700 | 70 |
| Latham’s Snipe* | 30,000 | 300 | 18* |
| Lesser Sand Plover | 180,000-275,000 | 1800 | 180 |
| Little Curlew | 110,000 | 1100 | 110 |
| Little Ringed Plover | 150,000 | 1500 | 150 |
| Long-toed Stint | 230,000 | 2300 | 230 |
| Marsh Sandpiper | 130,000 | 1300 | 130 |
| Oriental Plover | 230,000 | 2300 | 230 |
| Oriental Pratincole | 2,880,000 | 28,800 | 2880 |
| Pacific Golden Plover | 120,000 | 1200 | 120 |
| Pectoral Sandpiper | 1,220,000-1,930,000 | 12,200 | 1220 |
| Pin-tailed Snipe | 170,000 | 1700 | 170 |
| Red Knot | 110,000 | 1100 | 110 |
| Red-necked Phalarope | 250,000 | 2500 | 250 |
| Red-necked Stint | 475,000 | 4750 | 475 |
| Ruddy Turnstone | 30,000 | 300 | 30 |
| Ruff | 25,000-100,000 | 250 | 25 |
| Sanderling | 30,000 | 300 | 30 |
| Sharp-tailed Sandpiper | 85,000 | 850 | 85 |
| Swinhoe’s Snipe | 40,000 | 400 | 40 |
| Terek Sandpiper | 50,000 | 500 | 50 |
| Wandering Tattler | 10,000-25,000 | 100 | 10 |
| Whimbrel | 65,000 | 650 | 65 |
| Wood Sandpiper | 130,000 | 1300 | 130 |
Original link: Revision of the East Asian-Australasian Flyway Population Estimates for 37 listed Migratory Shorebird Species (Australian Government)
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