







| Kingdom | Phylum | Class | Order | Family |
|---|---|---|---|---|
| ANIMALIA | CHORDATA | AVES | Podicipediformes | Podicipedidae |
| Scientific Name: | Podiceps gallardoi | |||
| Species Authority: | Rumboll, 1974 | |||
Common Name/s:
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| Red List Category & Criteria: | Endangered A2bce+3bce+4bce ver 3.1 | |||||||||||||||||||||
| Year Assessed: | 2009 | |||||||||||||||||||||
| Assessor/s | BirdLife International | |||||||||||||||||||||
| Evaluator/s: | Bird, J., Butchart, S.(BirdLife International) | |||||||||||||||||||||
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Justification: This species has a very small and very rapidly declining population within a moderately small range. It is likely that birds may move between breeding sites on an annual basis but recent absences from former breeding sites are now thought to represent genuine declines. Therefore, the species has been uplisted to Endangered, and further survey work is required to determine population trends. |
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| History: |
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| Population: |
O'Donnell and Fjeldsa (1997) estimated the population as 3,000-5,000 individuals. Following recent and rapid declines the population is now assumed to be well below this figure but owing to difficulties in surveying its remote breeding grounds a precise estimate is unavailable.
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| Population Trend: |
Decreasing
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| Habitat and Ecology: |
During the breeding season, it inhabits basaltic lakes in the arid Patagonian steppes at elevations of 500-1,200 m4; saline and bitter-salt lakes are used by non-breeding flocks and at least some birds wintering on the Argentine coast2. Aquatic vegetation (mainly Myriophyllum elatinoides) on its breeding lakes is essential material for its floating nest and as habitat for several aquatic invertebrates that form its basic diet4. During the first week after hatching, chicks are fed with aquatic beetles (Limnaea spp.)4. It breeds in colonies of up to 130 pairs from October-March4, but has an exceedingly low reproductive rate with an average of 0.2 young reared per adult per year5. However, while potential resources for breeding are apparently limited, the resources for adult survival appear to be plentiful and under natural circumstances adult mortality may be extremely low5. It occasionally establishes colonies in areas marginal to its main range5.
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| Systems: | Freshwater |
| Major Threat(s): |
The two principal threats to the species appear to be climate change and the introduction of salmon and trout to private lakes on the Strobel plateau6. Recently the introduction of trout has been correlated with a decline in breeding numbers at certain lakes7,10. Surveys in 2006 found a number of lakes completely dry and that water levels at known breeding sites were 2-3 m lower than in previous years10. Anecdotal reports indicated reduced winter snowfall without a corresponding increase in precipitation at other times10. Excessive grazing by sheep (which causes erosion at lakeshores and limits the growth of emergent vegetation), predation by Kelp Gulls Larus dominicanus at some lakes, an inhospitable breeding climate and low breeding potential have been cited as threats1,5, but the species's life history strategy is apparently well adapted to these conditions3. The population may be limited by the carrying capacity of rather few lakes with good nest vegetation5. Volcanic eruptions in the breeding area may have a negative short-term effect because of heavy ash fall, but a long-term positive effect on the productivity of the wetlands5. There is oil exploitation on the potential migration route to the Atlantic6.
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| Conservation Actions: |
Conservation actions underway: The site where the species was discovered in 1974, Laguna Los Escarchados, was declared a reserve in 1979 but is now known to hold only a marginal population5, and six individuals were recorded within Perito Moreno National Park, Argentina in 1992. Its key breeding lakes in the core of its range lack any kind of legal protection, but the population stronghold on Meseta de Strobel is afforded some protection from its remoteness and inaccessibility1.
Continue monitoring at key sites at intervals of a few years5. Survey upland and coastal sites to identify wintering and staging sites5. Write and implement a species recovery plan. Work with landowners to raise awareness of the impacts on Hooded Grebes of introducing salmonids to lakes, and identify lakes where salmonids could be introduced without negatively impacting Hooded Grebes. Study the species's ecology to understand population movements. Identify breeding sites. Gather empirical data on population size and trends. Clarify the threats to the species and the reasons behind recent declines.
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| Citation: | BirdLife International 2009. Podiceps gallardoi. In: IUCN 2009. IUCN Red List of Threatened Species. Version 2009.2. <www.iucnredlist.org>. Downloaded on 09 February 2010. |
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