Red List of South African Species

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Endangered (EN)

Rationale

Extensive surveys by Greig and Burdett (1976) extended the distribution range of Chersobius boulengeri substantially, which led the authors to propose that the species is not rare, as was previously believed, but that individuals were seldom encountered because they were so well camouflaged. The conservation status of C. boulengeri was considered to be Least Concern on the 1996 IUCN Red List (TTWG 2014, 2017), but as possibly Vulnerable at a Tortoise and Freshwater Turtle Specialist Group Red Listing workshop in late 2013. It was subsequently listed as Near Threatened on the IUCN Red List in 2017 based on an earlier 2013 assessment (Hofmeyr and Baard 2014, Bates et al. 2014). Surveys conducted between 2005 and 2017 indicated that most localities (30 of 35) where populations previously occurred no longer harbor viable populations and that the species is no longer being found by farmers. Habitat destruction and degradation maps of South Africa (Hoffman et al. 1999) show that nearly 50% of the range of C. boulengeri is either moderately or severely degraded, which may explain the species’ decline. Chersobius boulengeri is associated with rocky outcrops in specific vegetation types, qualifying it as a habitat specialist, which increases its risk of extinction. The documented population declines will be exacerbated by the effects of climate change and associated vegetation change. Monitoring over recent decades showed that grasses are invading the Karoo, replacing the dwarf shrubs, with an increasing fire-hazard in the habitat (Stevens et al. 2015). The Nama-Karoo is considered the second most threatened biome in South Africa under all climate scenarios. Predictions are that savanna and desert vegetation will expand into large portions of the current biome (Driver et al. 2012; DEA 2013). Such changes would intensify grazing pressure by livestock and reduce food and cover for tortoises. Predation by baboons was high at one site visited during surveys (M. Hofmeyr pers. obs.) and crow predation may be on the increase (Juvik and Hofmeyr 2015). A serious new emerging threat involves shale gas exploration and development, which would require substantial large-scale infrastructure to support the drilling and operation of wells and extraction sites. Based on these factors, C. boulengeri is assessed as Endangered under criterion A4ace, based on an estimate of a reduction in population size of approximately 30% over the past 25 years (one generation), and a projected reduction of at least another 30% over the next 50 years (two generations), for a total reduction over three generations of approximately 60%.

Distribution

Chersobius boulengeri is endemic to South Africa, occurring from Bruintjieshoogte in the Eastern Cape to Touwsrivier in the Western Cape; the range in the Northern Cape extends north of Williston in the northwest and beyond Vosburg in the northeast (Hofmeyr and Baard, 2014, TTWG 2017).

Population trend

Trend

Chersobius boulengeri is a habitat specialist and population densities are low. Populations are isolated on rocky outcrops with specialized vegetation. We expect that their movement potential is low, similar to C. signatus (Loehr 2015). Between 2005 and 2017, we launched 10 separate surveys to localities where the species had been documented previously, covering 35 different sites and spending approximately 988 person-hours on searches (Loehr, Hofmeyr, and Juvik unpubl. data). We found a single site with a population that could be considered viable, four live tortoises and a few shells at four other sites, with no sign of the species at the remaining 30 sites. Our surveys covered approximately 50% of the species’ westerly distribution. During each field trip, farmers and their employees indicated that they seldom, or no longer, encountered these tortoises, or that they had never seen them on their farms or even in their region. Some farmers said that they used to find these tortoises in localized areas, demonstrating highly specialized habitat requirements. The results of our search efforts indicate that many populations have disappeared and that population numbers have declined significantly.

Threats

The main past and current threat to Chersobius boulengeri appears to be habitat degradation. Drought and agricultural overgrazing also threaten the species' habitat. Climate change maps indicate future changes under all scenarios to habitats in the southern and eastern distribution range of the species (Driver et al. 2012). Crows and baboons pose another threat because, due to the small size of the species, these predators can exploit adult tortoises. A serious new threat involves shale gas exploration, which would require substantial infrastructure to support the drilling and operation of wells and large-scale extraction sites.

Conservation

Chersobius boulengeri is included in CITES Appendix II (as Testudinidae spp.) and is protected in South Africa by provincial nature conservation ordinances and biodiversity laws at a regional level. The species is not protected at a national level by the National Environmental Management Biodiversity Act, 2004 (Act No. 10 of 2004). It is, or used to be, found in two protected areas in the Western Cape Province: Gamkapoort and Anysberg, and possibly in Karoo National Park. Conservation officers in the Northern, Western, and Eastern Cape provinces must be alerted to concerns about the species' status. Thereafter, local communities should be involved in determining the status of populations and the extent of population declines over the range of the species.

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