NT
Mountain Pipit Anthus hoeschi



Taxonomy

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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - -

Red List history
Year Category Criteria
2021 Near Threatened C1+2a(ii)
2017 Near Threatened C1
2016 Least Concern
2012 Least Concern
2009 Least Concern
2008 Least Concern
2004 Least Concern
2000 Lower Risk/Least Concern
1994 Lower Risk/Near Threatened
1988 Lower Risk/Least Concern
Species attributes

Migratory status full migrant Forest dependency does not normally occur in forest
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 33,300 km2 medium
Extent of Occurrence (non-breeding) 307,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 2500-9999 mature individuals poor suspected 2015
Population trend decreasing - suspected 2015-2025
Rate of change over the past 10 years/3 generations (longer of the two periods) 1-19% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 1-19% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 1-19% - - -
Generation length 2.21 years - - -
Number of subpopulations 1 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: Taylor et al. (2015) suggest that the global population of this species numbers less than 10,000 mature individuals, placed here in the range 2,500-9,999 mature individuals. Lesotho is reportedly a stronghold for this species, and it has been recorded in the highlands at densities of 50 singing males per 54 km transect (Kopij 2015a), 33 singing males per 61.2 km transect in Afro-montane grassland, and 54 singing males per 44.7km transect in Alti-mountain grassland (Kopij 2015a, 2015b). This species was not recorded in the foothills (Kopij 2015a) but it has been recorded in the Sehlabathebe National Park at densities of 30 singing males per 32 km transect (Kopij 2002).
Based on the species’s distribution, it is assumed that it functions as one subpopulation, and therefore that 100% of mature individuals are within the same subpopulation.

Trend justification: It is suspected that the species is declining overall due to habitat shifting caused by climate change, as temperatures in South Africa have been rising (van Wilgen et al. 2016). Taylor et al. (2015) suggest that the species's range may have declined by up to 40% between SABAP1 and SABAP2 (c.1991-c.2015). This would be equivalent to a decline of 19% over 10 years. However, Lee et al. (2017) suggest the range may have declined by 9% between SABAP1 and SABAP2. Therefore, the species is tentatively suspected to have declined in the range of 1-19% over 10 years, and based on the threat of habitat shifting from climate change, these rates are suspected to continue into the future.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Angola extant native yes yes
Botswana extant native yes
Congo, The Democratic Republic of the extant native yes yes
Lesotho extant native yes
Namibia extant native yes
South Africa extant native yes
Zambia extant native yes yes
Zimbabwe extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Lesotho Liqobong
Lesotho Mafika - Lisiu
Lesotho Sehlabathebe National Park
Lesotho Sehonghong and Matebeng
Lesotho Upper Quthing Valley
Lesotho Upper Senqu River
South Africa Golden Gate Highlands National Park
South Africa Maloti Drakensberg Park
South Africa Matatiele Nature Reserve

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Grassland Subtropical/Tropical High Altitude major resident
Shrubland Subtropical/Tropical High Altitude major breeding
Altitude 2000 - 3000 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Climate change & severe weather Habitat shifting & alteration Timing Scope Severity Impact
Ongoing Whole (>90%) Unknown Unknown
Stresses
Indirect ecosystem effects, Ecosystem degradation

Recommended citation
BirdLife International (2024) Species factsheet: Mountain Pipit Anthus hoeschi. Downloaded from https://datazone.birdlife.org/species/factsheet/mountain-pipit-anthus-hoeschi on 22/11/2024.
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 22/11/2024.