Red List of South African Species

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Least Concern (LC)

Rationale

This species has a wide distribution across the assessment region, occurs in many protected areas – including Kgalagadi Transfrontier Park – and there are no major threats that could cause range-wide population declines. Habitat available for Ground Squirrels is stable if not expanding, as they can exist on overgrazed lands, and thus the expansion of livestock and wildlife ranching may benefit this species. Furthermore, it is a resilient species, adapting its social organisation, space use and breeding to climactic fluctuations, and thus will likely be able to adapt to climate change. No specific interventions are necessary at present.

The Damara Ground Squirrel (Xerus princeps) is Not Evaluated in this revision as, although it may marginally exist in South Africa (for example, at Augrabies National Park; J. Waterman pers. obs.), it is an extreme edge of range species and there is no evidence of a breeding population. It is therefore considered vagrant. However, it may become more prevalent within South Africa (inhabiting mountains, cliffs and gorges) as climate change increases arid conditions, and may thus require a reassessment in future.

Regional population effects: The species’ range is continuous throughout the arid areas of southern Africa and thus dispersal is possible across Namibia and Botswana. Populations in Namibia and Botswana are not expected to decline.

Distribution

This species is restricted to southern Africa, south of the Cunene and Zambezi Rivers (Griffin & Coetzee 2008). It is distributed widely in Namibia, except where replaced by X. princeps in the north-west (Skinner & Chimimba 2005), and is absent from coastal regions. It is confined to the semi-desert Kalahari in Botswana. In South Africa, it occurs mainly in the arid interior, being widely distributed in the arid parts of North West (Power 2014), Free State, the Northern Cape (northern and north-eastern parts of the province) provinces, and southwards to the Graaff Reinet District in the Eastern Cape, which marks the most southerly limit of its distribution (Skinner & Chimimba 2005). There are isolated subpopulations in northern Limpopo Province (I. Gaigher & W. Collinson pers. obs. 2015; Figure 1). It also occurs in western Lesotho (Lynch 1994). The greater part of its range is within the Nama-Karoo and Succulent Karoo biomes in areas with a mean annual rainfall of 100–500 mm (Skinner & Chimimba 2005). The species’ range is continuous throughout the arid areas of southern Africa, except in areas of the western Namib (Skurski & Waterman 2005), which is reflected by mitochondrial DNA work that suggests all subpopulations are genetically connected and represent only a single species (Herron et al. 2005).

Population trend

Trend

This is a common species wherever it occurs. In Namibia, it exists at densities of c. 400 individuals / km2 and, in S.A. Lombard Nature reserve, North West Province, the density is higher (J. Waterman unpubl. data). The population is considered stable based on no net decline in habitat.

Local declines may be expected in areas where Black-backed Jackal (Canis mesomelas) numbers are high due to the removal of apex predators. For example, at three sites in the Northern Cape, there was a negative relationship between Ground Squirrel and Black-backed Jackal abundance (Bagniewska & Kamler 2014).

Threats

There are no major identified threats that could cause population declines. It is considered to be an agricultural pest in some parts of its range (Griffin & Coetzee 2008), but has not been reported as such within the assessment region (Power 2014). There are localised complaints about damage to gravel and farm roads as a result of burrow formations (B. Wilson unpubl. data). They tend to prefer Schmidtia kalaharensis (J. Waterman unpubl. data), a grass that is characteristic of degraded lands, such as where there is overgrazing. Thus, livestock and wildlife ranching, contrary to what was reported in the previous assessment (Friedmann & Daly 2004), are not threats but are probably beneficial to this species.

Uses and trade

There is no evidence for significant utilisation of this species.

Conservation

The species is common in many protected areas across the assessment region, including Kgalagadi Transfrontier Park. Additionally, the expansion of wildlife ranches across the arid parts of its range may be expanding habitat for this species as it occurs in areas that have been overgrazed or where there are high densities of grazers (J. Waterman unpubl. data). No specific conservation interventions are necessary at present.

Recommendations for land managers and practitioners: None

Research priorities: An ongoing research project (since 2002) is being conducted in S. A. Lombard Nature Reserve, North West Province, by Prof. Jane Waterman. Research areas include parasitology (Hillegass et al. 2008, 2010), and its energetic costs (Scantlebury et al. 2007); physiology (Scantlebury et al. 2012), including the effects of hormone physiology and resource availability on reproduction (Jackson et al. 2007; Pettitt et al. 2008; Pettitt & Waterman 2011); gender-bias in immunology (Manjerovic & Waterman 2012); effectiveness of chemical immobilization and anaesthesia (Joubert et al. 2011); and behavioural ecology, including interactions with predators and group dynamics (Belton et al. 2007; Unck et al. 2009).

Research priorities regarding the conservation assessment are as follows:
  • The abundance and distribution of the species given various grazing intensities of both livestock and wildlife ranching.
  • The efficacy of this species as an ecological engineer in enhancing small mammal abundance, invertebrate abundance and plant diversity.
Encouraged citizen actions:
  • Report sightings of this species, especially outside protected areas, on virtual museum platforms (for example, iSpot and MammalMAP).

Lead agencies, Partners and Funders

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