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Willan’s Vlei Rat

Otomys willani

2025 Red list status

Least Concern

Decline
Regional Population Trend

Unknown

Change compared
to 2016

New Assessment 

Overview
Red list assessment
Regional Distribution and Occurrence
Climate change
Population information
Population genetics
Habitats and ecology
Use and Trade
Threats
Conservation
Bibliography

Overview

Otomys willani – Taylor et al. 2020 

ANIMALIA – CHORDATA – MAMMALIA – RODENTIA – MURIDAE – Otomys – willani 

Common Names: Willan’s Vlei Rat (English)

Synonyms: None 

Taxonomic Note: Formerly part of O saundersiae (which is a synonym of O. irroratus) and then O. karoensis, but Taylor et al. (2020 showed that Eastern Cape specimens of O. karoensis s.l. were phylogenetically and morphologically highly distinct from O. karoensis s.s. from the Western Cape (of which the sister species is O. laminatus).Three very small-sized specimens from the Free State, noted as O. cf. karoensis sp. 2 by Taylor et al. (2020) seem to represent a genetically distinct, undescribed species that is probably more widespread in the Free State, including Golden Gate Highlands National Park where two similar-sized and genetically unique individuals were captured and released in 2019 (Ramoejane, unpublished data). 

Red List Status: LC – Least Concern

Assessment Information

Assessors: Taylor, P.1 & da Silva, J.M.2 

Reviewer: Oosthuizen, M.3 

Institutions: 1University of the Free State,2South African National Biodiversity Institute, 3University of Pretoria 

Assessment Rationale 

This species is listed as Least Concern as it probably does not reach any EOO or AOO thresholds. 

Reasons for Change 

Reason(s) for Change in Red List Category from the Previous Assessment: No change, new assessment 

Red List Index 

Red List Index: New assessment 

Recommended Citation: Taylor P & da Silva JM. 2025. A conservation assessment of Otomys willani. In Patel T, Smith C, Roxburgh L, da Silva JM & Raimondo D, editors. The Red List of Mammals of South Africa, Eswatini and Lesotho. South African National Biodiversity Institute and Endangered Wildlife Trust, South Africa.

Regional Distribution and occurrence

Geographic Range 

The species occurs along the Southern Great Escarpment from the Sneeuberg to the southern Drakensberg at elevations > 2000 m a.s.l., from the Karoo National Park in the west to Giant’s Castle in KwaZulu-Natal Province in the east (Taylor et al. 2020).  

Elevation / Depth / Depth Zones 

Elevation Lower Limit (in metres above sea level): 2000 m 

Elevation Upper Limit (in metres above sea level): 2700 m 

Depth Lower Limit (in metres below sea level): N/A 

Depth Upper Limit (in metres below sea level): N/A 

Depth Zone: N/A 

Map

Figure 1. Distribution records for Willan’s Vlei Rat (Otomys willani) within the assessment region (South Africa, Eswatini and Lesotho). Note that distribution data is obtained from multiple sources and records have not all been individually verified.

Biogeographic Realms 

Biogeographic Realm: Afrotropical 

Occurrence 

Countries of Occurrence 

Country  Presence  Origin  Formerly Bred  Seasonality 
South Africa  Extant  Native    Resident 

Large Marine Ecosystems (LME) Occurrence 

Large Marine Ecosystems: (Not specified) 

FAO Area Occurrence 

FAO Marine Areas: (Not specified) 

 

 

Climate change

Like O. auratusO. willani is a grassland montane species that is projected to decline in range with climate change by 2050 (Taylor et al. 2016). 

Population Information

There is currently no information available for the population size or densities of this species.  

Population Information 

Continuing decline in mature individuals? (Not specified) 

Extreme fluctuations in the number of subpopulations: (Not specified) 

Continuing decline in number of subpopulations: (Not specified) 

All individuals in one subpopulation: (Not specified) 

Number of mature individuals in largest subpopulation: (Not specified) 

Number of Subpopulations: (Not specified) 

Quantitative Analysis 

Probability of extinction in the wild within 3 generations or 10 years, whichever is longer, maximum 100 years: (Not specified) 

Probability of extinction in the wild within 5 generations or 20 years, whichever is longer, maximum 100 years: (Not specified) 

Probability of extinction in the wild within 100 years: (Not specified) 

 

Population Genetics

A recent phylogenetic study revealed the existence of a unique lineage of Otomys previously attributed to O. karoensis (currently O. willaniTaylor et al. 2020). No evidence of separate subpopulations, or genetic structure was detected within the species (Taylor et al. 2020).  Consequently, the species is thought to exist as a single metapopulation within the assessment region. Because no information exists related to population sizes or densities, estimates of effective population size (Ne) cannot be quantified at this time. 

Habitats and ecology

This species occupies open grasslands between about 2000 m and 2700 m (Taylor et al. 2020). At higher elevations, they co-occur with Otomys sloggetti 

Ecosystem and cultural services: Vlei rats are an important food source for a number of mammalian predators such as Serval (Leptailurus serval), Marsh Owls (Asio capensis) and Barn Owls (Tyto alba) (Skinner and Chimimba 2005, Monadjem et al. 2015).  

IUCN Habitats Classification Scheme 

Habitat  Season  Suitability  Major Importance? 
4.7. Grassland -> Grassland – Subtropical/Tropical High Altitude    Suitable   
5.4. Wetlands (inland) -> Wetlands (inland) – Bogs, Marshes, Swamps, Fens, Peatlands    Suitable   
       

Life History 

Generation Length: (Not specified) 

Age at Maturity: Female or unspecified: (Not specified) 

Age at Maturity: Male: (Not specified) 

Size at Maturity (in cms): Female: (Not specified) 

Size at Maturity (in cms): Male: (Not specified) 

Longevity: (Not specified) 

Average Reproductive Age: (Not specified) 

Maximum Size (in cms): (Not specified) 

Size at Birth (in cms): (Not specified) 

Gestation Time: Likely around 40 days as in other Otomys species 

Reproductive Periodicity: (Not specified) 

Average Annual Fecundity or Litter Size: (Not specified) 

Natural Mortality: (Not specified) 

Does the species lay eggs? no 

Does the species give birth to live young: yes 

Does the species exhibit parthenogenesis: no 

Does the species have a free-living larval stage? no 

Does the species require water for breeding? no 

Movement Patterns 

Movement Patterns: (Not specified) 

Congregatory: (Not specified) 

Systems 

System: Terrestrial 

 

General Use and Trade Information

This species is not known to be utilised or traded. 

Local Livelihood: (Not specified) 

National Commercial Value: (Not specified) 

International Commercial Value: (Not specified) 

End Use: (Not specified) 

Is there harvest from captive/cultivated sources of this species? (Not specified) 

Harvest Trend Comments: (Not specified) 

 

Threats

There are no major threats known, although habitat loss and degradation from wetland drainage, grassland loss and exotic vegetation, are all suspected to be minor threats. Additionally, climate change may represent an emerging threat to the montane grassland habitats that this species predominantly occupies. Climate modelling for similarly mesic-adapted Otomys species reveals significant reductions in area of occupancy by 2050 (Taylor et al. 2016). More research is needed to determine specific effects of climate change on O. willani.   
 
Wetlands are the most threatened ecosystem in South Africa (Driver et al. 2012). The South African National Land-Cover change report found a 32.8% decline in natural wetlands nationally from 1990-2013/14, which is a combination of both genuine wetland loss through anthropogenic activities and the generally drier conditions currently that in 1990 (GeoTerraImage 2015).  

Conservation

This species occurs within at least five protected areas within the Western Cape (Karoo National Park), Eastern Cape (Asante Sana Nature Reserve, Mountain Zebra National Park, Grassland National Park) and KwaZulu-Natal (uKhahlamba-Drakensberg National Park). Ongoing degradation of wetlands, over-grazing and soil erosion are likely to severely negatively impact habitat quality. Although no specific interventions are necessary at present, the conservation and restoration of wetlands and grasslands would benefit this species. The following interventions are thus encouraged:  

  • Using previously cultivated areas for development instead of remaining natural areas. 
  • Land managers should maintain a vegetation buffer around wetlands to reduce impacts of land-use practices (Driver et al2012). 

 

Bibliography

Bowland, A.E. and Perrin, M.R. 1989. The effect of overgrazing on the small mammals in Umfolozi Game Reserve. Zeitschrift für Säugetierkunde 54: 251–260. 

Bowland, J.M. 1990. Diet, home range and movement patterns of serval on farmland in Natal. Department of Zoology and Entomology, University of Natal. 

Driver, A., Sink, K.J., Nel, J.N., Holness, S., Van Niekerk, L., Daniels, F., Jonas, Z., Majiedt, P.A., Harris, L. and Maze, K. 2012. National Biodiversity Assessment 2011: An assessment of South Africa’s biodiversity and ecosystems. Synthesis Report. South African National Biodiversity Institute and Department of Environmental Affairs, Pretoria, South Africa. 

GeoTerraImage. 2015. 1990-2013/14 South African National Land-Cover Change. DEA/CARDNO SCPF002: Implementation of Land-Use Maps for South Africa. Project Specific Data Report. 

IUCN. 2017. The IUCN Red List of Threatened Species. Version 2017-2. Available at: www.iucnredlist.org. (Accessed: 14 September 2017). 

Meester, J.A.J., Rautenbach, I.L., Dippenaar, N.J. and Baker, C.M. 1986. Classification of Southern African Mammals. Monograph number 5. Transvaal Museum , Pretoria, South Africa. 

Monadjem, A., Taylor, P.J., Denys, C. and Cotterill, F.P.D. 2015. Rodents of Sub-Saharan Africa – a biogeographic and taxonomic synthesis. De Gruyter, Berlin/Munich/Boston. 

Pence, G.Q.K. 2012. Contribution of C.A.P.E. Business and Biodiversity Initiatives to conservation of critical biodiversity, landscape connectivity and ecological support areas: Post-baseline assessment (2010). A Green Choice Alliance project report. Conservation South Africa, Kirstenbosch, South Africa. 

Skinner, J.D. and Chimimba, C.T. (eds). 2005. The Mammals of the Southern African Subregion. Cambridge University Press, United Kingdom, Cambridge. 

Taylor, P.J., Nengovhela, A., Linden, J. and Baxter, R.M. 2016. Past, present, and future distribution of Afromontane rodents (Muridae: Otomys) reflect climate-change predicted biome changes. Mammalia 80: 359–375. 

Taylor, P. J., Kearney, K., Dalton, D., Mataruse, G., Kelly, C. M. R. and Barker, N. P. 2020. Biomes, geology and past climate drive speciation of laminate-toothed rats on South African mountains (Murinae: Otomys). Zoological Journal of the Linnean Society 189: 1046–1066, https://doi.org/10.1093/zoolinnean/zlz134