Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A., Fishpool, L.D.C., Boesman, P. and Kirwan, G.M. 2016. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 2: Passerines. Lynx Edicions and BirdLife International, Barcelona, Spain and Cambridge, UK.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2019 | Near Threatened | A2c+4c |
2018 | Vulnerable | A2cde |
2016 | Vulnerable | A2cde |
2012 | Vulnerable | A2cde+4cde |
2008 | Vulnerable | A2c,d,e |
2004 | Vulnerable | |
2000 | Vulnerable | |
1994 | Lower Risk/Near Threatened | |
1988 | Lower Risk/Least Concern |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | 105 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 14,800 km2 | medium |
Number of locations | 11-100 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 100000-499999 mature individuals | poor | estimated | 2018 |
Population trend | unknown | poor | suspected | 1998-2008 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Generation length | 4.4 years | - | - | - |
Number of subpopulations | 5 | - | - | - |
Population justification: Point counts on Montserrat found c.1,200 individuals at 88 stations in the Centre Hills in 2016 (Bambini et al. 2017). As these stations covered only 20-40% of the available forest habitat (Oppel et al. 2014), the population on Montserrat could be between 1,500 - 10,000 individuals (1,000-7,000 mature individuals). A recent study based on surveys and habitat mapping on Guadeloupe has suggested that previous population estimates have been substantial underestimates, with the Guadeloupe population estimated at 46,900 – 49,500 pairs (93,800 – 99,000 mature individuals; Eraud et al. 2012). However, the estimate was based on distance sampling which can be highly inaccurate in dense tropical forests given that most Forest Thrush detections are aural. The sizes of the populations on Dominica and St Lucia are unknown, although the latter is assumed to be very small, if not zero. The total population is therefore placed in the band 100,000-499,999 mature individuals.
Trend justification: The species underwent a significant population reduction over recent decades, particularly during 1995-1997, when the range on Montserrat was reduced by two-thirds by the effects of volcanic eruptions and ash fall (G. Hilton in litt. 2000). However, more recent data has suggested that the species’s population may no longer be declining. In December 1999, the population on Montserrat was estimated at 3,100 birds (Arendt et al. 1999), representing an increase of c.50% since December 1997, with further increases up until 2004, followed by a period of stability and further increased between 2011 and 2016 (Parashuram 2013, S. Oppel in litt. 2016, Bambini et al. 2017, S. Oppel in litt. 2019). Montserrat thus holds a small proportion of the global population, which is stable or slowly increasing. On St Lucia, there has been just one recent record (at Des Chassin in 2007), but it was considered numerous in the late 19th century, indicating a serious long-term decline, if not extirpation (Keith 1997, B. Ibene in litt. 2014, L. John in litt. 2016, S. Oppel in litt. 2019). Little is known about population trend on Dominica, but the population size is likely low. As a consequence of hurricane Maria, which hit the island in 2017, the population may likely have declined further, though it is still observed there (see recent records on eBird; eBird 2018). The majority of the population is found on Guadeloupe (Eraud et al. 2012), and all evidence suggests only a very slow decline. Precautionarily, it is assumed that the historic decline on St Lucia, the potentially large declines on Dominica and the very slow declines on Guadeloupe sum up to such a magnitude that the species’s global population is currently in decline at a rate approaching 30% over three generations.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Dominica | extant | native | yes | |||
Guadeloupe (to France) | extant | native | yes | |||
Montserrat (to UK) | extant | native | yes | |||
St Lucia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Dominica | Morne Diablotin National Park |
Dominica | Morne Trois Pitons National Park |
Guadeloupe (to France) | Forestry massif of Basse-Terre island |
Guadeloupe (to France) | Grand Cul-de-Sac Marin's eastern coastline |
Montserrat (to UK) | Centre Hills |
Montserrat (to UK) | Northern Forested Ghauts |
Montserrat (to UK) | South Soufriere Hills |
St Lucia | Castries and Dennery Waterworks Reserve and Marquis |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 0 - 1400 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
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Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
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Geological events | Volcanoes | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Minority (<50%) | Rapid Declines | Past Impact | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Herpestes javanicus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Molothrus bonariensis | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Unspecified species | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
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Invasive and other problematic species, genes & diseases | Problematic native species/diseases - Turdus nudigenis | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | No decline | Low Impact: 4 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Forest Thrush Turdus lherminieri. Downloaded from
https://datazone.birdlife.org/species/factsheet/forest-thrush-turdus-lherminieri on 23/12/2024.
Recommended citation for factsheets for more than one species: BirdLife International (2024) IUCN Red List for birds. Downloaded from
https://datazone.birdlife.org/species/search on 23/12/2024.