Taxonomic note
Hemimacronyx chloris (del Hoyo and Collar 2016) was previously placed in the genus Anthus following Dowsett & Forbes-Watson (1993); Sibley & Monroe (1990, 1993).
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 |
---|---|---|
- | - | A3c; C2a(i); D1 |
Year | Category | Criteria |
---|---|---|
2021 | Vulnerable | A3c; C2a(i); D1 |
2018 | Vulnerable | A3c; C2a(i); D1 |
2016 | Vulnerable | A3c; B1ab(i,ii,iii,iv,v); D1 |
2012 | Vulnerable | A3c;B1ab(i,ii,iii,iv,v) |
2008 | Vulnerable | A3c; B1a+b(i,ii,iii,iv,v); C1 |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | does not normally occur in forest |
Land-mass type |
continent |
Average mass | 25 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 163,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 424-1210 mature individuals | medium | estimated | 2016 |
Population trend | decreasing | medium | inferred | - |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 20-29% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Generation length | 3 years | - | - | - |
Number of subpopulations | 2-100 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: Barnes (2000) estimated the population to be 2,500-6,500 individuals, roughly equivalent to 1,700-4,300 mature individuals. In view of substantial range reductions since Barnes's assessment, and assuming concomitant population declines, Little (2015) used a conservative estimate of a 20% population decrease, estimating the population at 2,000-4,800 individuals. Estimates based on extensive field work to determine the summer breeding range of this species, and using species range figures and average home range sizes, have resulted in population estimates of 607-1,730 individuals, approximately equating to 424-1,210 mature individuals (Pietersen et al. 2018).
Trend justification: The species's population is inferred to be declining due to ongoing loss and degradation of its grassland habitat (Pietersen et al. 2018). Habitat loss through rangeland degradation and conversion to agriculture is ongoing (Pietersen et al. 2018). Survey work does suggest, though, that the population may be stable in some local patches (R. Colyn in litt. 2017), so past declines are tentatively suspected to be moderately rapid. The rate of decline is expected to increase in the next ten years, with climate change potentially impacting 90% of the species's range by 2050 (R. Colyn in litt. 2017).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Lesotho | extant | native | yes | |||
South Africa | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Lesotho | Sehlabathebe National Park |
South Africa | Alexpan |
South Africa | Golden Gate Highlands National Park |
South Africa | Grasslands |
South Africa | Maloti Drakensberg Park |
South Africa | Matatiele Nature Reserve |
South Africa | Steenkampsberg |
South Africa | Umgeni Vlei Nature Reserve |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Arable Land | marginal | resident |
Artificial/Terrestrial | Pastureland | suitable | non-breeding |
Grassland | Subtropical/Tropical High Altitude | major | breeding |
Savanna | Dry | suitable | non-breeding |
Altitude | 1400 - 2400 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Agro-industry farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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Agriculture & aquaculture | Wood & pulp plantations - Scale Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
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Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Whole (>90%) | Very Rapid Declines | Medium Impact: 7 | ||||||
|
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Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
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Invasive and other problematic species, genes & diseases | Problematic native species/diseases - Named species | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Natural system modifications | Fire & fire suppression - Trend Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
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Recommended citation
BirdLife International (2024) Species factsheet: Yellow-breasted Pipit Hemimacronyx chloris. Downloaded from
https://datazone.birdlife.org/species/factsheet/yellow-breasted-pipit-hemimacronyx-chloris on 26/12/2024.
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 26/12/2024.