CHECKLIST

 

South African National Survey of Arachnida: A checklist of the spiders (Arachnida, Araneae) of the Tswalu Kalahari Reserve in the Northern Cape province, South Africa

 

 

Anna S. Dippenaar-Schoeman^{I, II}; Charles R. Haddad^III; Robin Lyle^I; Leon N. Lotz^IV; Stefan H. Foord^II; Rudy Jocque^V; Peter Webb^VI

^IBiosystematics Arachnology, ARC - Plant Protection Research Institute, South Africa
^IIDepartment of Zoology, University of Venda, South Africa
^IIIDepartment of Zoology & Entomology, University of the Free State, South Africa
^IVDepartment of Arachnology, National Museum Bloemfontein, South Africa
^VRoyal Museum for Central Africa, Tervuren, Belgium
^VISouth African National Survey of Arachnida, Pretoria, South Africa

Correspondence

 

 

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ABSTRACT

One of the aims of South African National Survey of Arachnida (SANSA) is to survey protected areas to obtain species-specific information and compile inventories to determine species distribution patterns and evaluate their conservation status for Red Data assessments. The aim of this study, the first in a series of surveys of the Diamond Route Reserves, was to compile the first checklist of the spider species in the Northern Cape at the Tswalu Kalahari Reserve. Spiders were collected during three survey periods (2005−2013) using different collecting methods to sample both the ground and field layers. In total, 32 families represented by 108 genera and 136 species have been collected so far. The most species-rich families are the Salticidae (20 spp.) and Thomisidae (18 spp.), followed by the Gnaphosidae and Araneidae (11 spp. each), while nine families are represented by singletons. The free-living wandering spiders represent 97 spp., while 39 spp. are web-builders. Information on spider guilds, endemicity value and conservation status are provided. The Tswalu Kalahari Reserve protects approximately 6.1% of the total South African spider fauna, while 24.3% of the species found in the reserve are South African endemics, of which 5.9% are Northern Cape endemics. Approximately 6.0% of the species sampled are possibly new to science or represent new records for South Africa.
CONSERVATION IMPLICATIONS: The Tswalu Kalahari Reserve falls within the Savanna Biome in the Northern Cape province. Only one spider species was previously known from the reserve; a further 135 spp. are reported for the first time, with 5.9% of the species being Northern Cape endemics and 24.3% South African endemics. Approximately 6.0% of the species may be new to science or represent new records for South Africa.

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Introduction

The South African National Survey of Arachnida (SANSA) was initiated in 1997, with the main aim of making inventories of the arachnid fauna of South Africa (Dippenaar-Schoeman & Haddad 2006; Dippenaar-Schoeman et al. 2015). SANSA has several focus areas, such as arachnid diversity in floral biomes, agroecosystems and protected areas. Species distribution data are an essential information resource needed for the conservation assessments used to compile a Red Data List of the Arachnida of South Africa (Lyle & Dippenaar-Schoeman 2015). Surveys are needed to obtain species-specific information, and yield new, rare and/or endemic species and resources for these existing protected areas. The publication of these species distribution records formed the basis of the first spider atlas and national species list (Dippenaar-Schoeman et al. 2010; Dippenaar-Schoeman 2013).

This study presents the results of SANSA sampling in the Tswalu Kalahari Reserve (TKR), falling within the arid parts of the Savanna Biome (Foord, Dippenaar-Schoeman & Haddad 2011a). The reserve is an E. Oppenheimer & Son property situated in the Northern Cape (Lyle & Dippenaar-Schoeman 2013). This is the first survey of the arachnid fauna of protected areas in the Northern Cape province and the first spider checklist for the TKR. Information on spider guilds, their habitat preference, web types, and endemicity index and conservation status are provided. Checklists for several of the protected areas in South Africa have been published but none for the Northern Cape (McGeoch et al. 2011; Dippenaar-Schoeman et al. 2015).

 

Research method and design

Study area and period

Tswalu Kalahari Reserve (27°13'30''S, 22°28'40''E; 930 m a.s.l.) is the largest (> 100 000 hectares) privately owned wildlife reserve in South Africa. It lies in the Northern Cape province, at the foot of the Korannaberg Mountains (Figure 1). Kuruman is the closest large town, some 140 km east of Tswalu.

Tswalu Kalahari Reserve includes vegetation described by Low and Rebelo (1998) as shrubby Kalahari dune bushveld, Kalahari plains bushveld and Kalahari mountain bushveld areas of the Savanna Biome (Figure 2a-d). Acocks (1988) described the area as Kalahari Thornveld. The reserve is characterised in certain areas by scattered shrubs and well-developed grass layers, in other areas by a well-developed tree layer and moderately developed grass and shrub layers, and by a poorly developed tree layer and moderately developed grass layers on the mountains and hills (Van Rooyen 1999). Some dominant plant species include the trees Vachellia erioloba, Boscia albitrunca and Terminalia sericea. The four main soil types in the TKR are poorly structured red soils with a high base status; well-drained red, sandy soils with a high base status; red and yellow, well-drained sandy soils with a high base status; and rocky areas with little or no soil (Van Rooyen 1999)

The climate of TKR is highly variable and falls in the summer rainfall area of southern Africa (Low & Rebelo 1998), with a relatively high rainfall occurring from October to April but with a distinct peak in March. The mean annual rainfall is 253.3 mm. The dry season occurs from May to September, with an average of less than 10.0 mm during this period. The peak dry season occurs from June to August, with little or no rainfall.

Sampling methods and identification

Material from three surveys (Table 1) was used to compile the first checklist of the spiders of TKR (Appendix 1). During the first visit to the reserve, spiders were collected ad hoc in all five habitats in the reserve (Figure 1) using a variety of methods, and no set protocol was followed. The second and third surveys were carried out using the standardised protocol devised for SANSA and described in detail by Haddad & Dippenaar-Schoeman (2015). It can be briefly summarised as follows: four representative habitats in a selected degree-square grid were selected by the field work manager, in this case the third author, and sampled by a team of four collectors. During the second and third surveys, sampling was carried out in grass layer around hills forming part of the Korannaberg-Langeberg Mountain Bushveld, Olifantshoek Plains Thornveld, Gordonia Plains Shrubland and Kathu Bushveld (Figure 1).

 

 

In each of these habitats sampled using the SANSA protocol, 500 beat samples were taken from woody vegetation using a beating sheet and beating stick; 500 sweep samples were taken from grasses and herbaceous vegetation using a sweep net; 50 pitfall traps (buckets with diameter of 135 mm) were set out 2 m apart and kept open for 3-4 days; ten leaf litter samples were taken and sifted over a white sheet using a steel sieve with a mesh spacing of 9 mm. Further, in each habitat, all four team members conducted 2 h of hand collecting during the day from beneath logs, rocks and bark and from vegetation. Night collecting (2 h per person) was done in all four habitats, as opposed to the single habitat required by the SANSA protocol. Winkler traps were used to extract leaf litter samples taken in a single habitat (Olifantshoek Plains Thornveld) during the second survey only; this method yielded poor results and was not used during the third survey.

All of the material sampled for each of the above methods was preserved in 70% ethanol, except for pitfall traps, in which propylene glycol was used as a preservative. Once the pitfalls were removed from the soil, the material was sieved, and the arachnids removed and preserved in 70% ethanol.

Species determinations were performed by several of the authors. Voucher specimens are deposited in the National Collection of Arachnida housed at the ARC-Plant Protection Research, Pretoria (NCA), and at the National Museum in Bloemfontein (NMBA). Only the generic names were included in the checklist when immature specimens were sampled and in those cases where the family lacks taxonomic resources to make species level identifications possible.

Functional groups

Spiders often live in distinct microhabitats with limitations imposed by contrasting biotic and abiotic factors. Species can be categorised into particular functional groups or guilds, based on our knowledge of their habitat and microhabitat preferences, as well as their diets and hunting strategies (Foord et al. 2011a). This provides valuable ecological information that helps in better understanding the utilisation of habitat structures by different taxa. In general, spiders can be divided into species that are largely or entirely reliant on silk to construct webs to capture prey (web-builders, WB) and those that actively search for prey or ambush prey from burrows or on vegetation (wanderers, W). Each of these two major guilds is divided into several subcategories based on the substrates they utilise or the web types that they construct (Table 2).

 

 

Endemicity value

The conservation status of species is important, and as part of the First Atlas of South African Spiders (Dippenaar-Schoeman et al. 2010), an endemicity index was provided for each species (Table 3, Appendix 1) based on its current distribution. Seven endemicity categories were considered: 6 = endemic, known only from type locality or one locality only; 5 = known from one province only, wider than type locality; 4 = known from two adjoining provinces only; 3 = South Africa, known from more than two provinces or two provinces not adjoining; 2 = southern Africa (south of Zambezi and Kunene Rivers); 1 = Afrotropical Region; 0 = Africa and wider.

 

 

Regarding conservation status, species that were only recorded from immatures or that represent new taxa were not evaluated, and are considered to be data deficient for taxonomic reasons (DDT). Species with a broad distribution (categories 0-2) were considered to be of Least Concern (LC); those of categories 3 and 4 were considered to be South African endemics (SAE); and those of category 5 were considered to be Northern Cape endemics (NCE). No Reserve Endemics (RE, category 6) have been recorded from TKR yet.

Photography

As part of SANSA, a photographic Virtual Museum was developed to access photographs of arachnid species (Dippenaar-Schoeman, Lyle & Van den Berg 2012; Dippenaar-Schoeman et al. 2015). Spiders sampled during the last surveys at TKR were photographed by the last author. A photo gallery of the spiders will be made available on the SANSA website. Images can also be viewed at http://www.arc.agric.za:8080/Default.

Ethical considerations

Permission to collect arachnids in the Northern Cape province was obtained from the Northern Cape Department of Environment and Nature Conservation.

 

Results and discussion

Spider biodiversity and endemicity

Thirty-two spider families represented by 108 genera and 136 spp. were collected from TKR between 2006 and 2013 over a total of 16 sampling days (Appendix 1, Table 4). Except for one species, Tusitala barbata Peckham & Peckham, 1902 (Salticidae), the rest of the species are reported from the reserve for the first time (Azarkina & Foord 2015). Although the Northern Cape is South Africa's largest province, covering 29.7% of the land area, only 1990 records sampled from 124 sites in the Northern Cape are accessioned in the SANSA database, represented by 490 spp. from 49 families (Dippenaar-Schoeman et al. 2015).

 

 

The Northern Cape province has been less intensively sampled than the other provinces. Except for the field guide on the spiders of the Kalahari (Dippenaar-Schoeman & Van den Berg 2010), no surveys from protected areas in the province have been published. Several surveys are underway in reserves (Benfontein, Rooipoort and Oryx Nature Reserves) and in the Augrabies, Richtersveld and Namaqua National Parks (Lyle & Dippenaar-Schoeman 2013; Dippenaar-Schoeman 2014a). The only published results are surveys in pistachio orchards in the arid Nama Karoo near Prieska (Haddad & Dippenaar-Schoeman 2005, 2006; Haddad, Dippenaar-Schoeman & Pekár 2005; Haddad, Louw & Dippenaar-Schoeman 2004; Haddad, Louw & Pekár 2008), where a total of 143 spp. from 31 families were collected (Foord et al. 2011a). In a second study, Lyons (2009) conducted a broad-scale survey of arthropods in restored alluvial diamond mining sites in the Succulent Karoo of the Northern Cape, in which 21 spider families and 51 spp. were sampled.

Based on these results and information from the SANSA database, the number of species sampled in reserves and parks in the Northern Cape is much lower (80-140 spp.) compared to Limpopo reserves, which average 228 spp. per reserve, ranging between 175 and 286 spp. (Foord et al. in prep.).

Of the 136 spp. sampled, ten spp. (7.4%) were DDT and could not be identified to species level, of which four spp. were immature and six spp. are possibly new to science (Appendix 1, Table 3). However, these putative new species are representatives of species-rich families, and only after revisionary studies would it be possible to tell whether they are indeed new to science. No species sampled from TKR thus far can be considered RE. Only the South African endemic species falling into categories 3-6 (33 spp., 24.3%) need to be evaluated using the IUCN criteria. The majority of the species sampled (93 spp.) can be listed as LC, having a distribution throughout southern Africa or wider (Table 3).

Seven Northern Cape endemic species are protected in the TKR: Ancylotrypa pusilla Purcell, 1903 (Cyrtaucheniidae) (Figure 3a); Dresserus laticeps Purcell, 1904 (Eresidae) (Figure 3b); Allocosa aurichelis Roewer, 1959 (Lycosidae) (Figure 3c); Aelurillus cristatopalpus Simon, 1902 (Salticidae); Evarcha brinki Haddad & Wesołowska, 2011 (Salticidae); Ariadna jubata Purcell, 1904 (Segestriidae) (Figure 3d) and Histagonia deserticola Simon, 1895 (Theridiidae).

During this study, Ibala okorosave Fitzpatrick, 2009 (Gnaphosidae) was recorded from South Africa for the first time, and the first adult specimens of the monotypic genus Mallinus Simon, 1893 (Zodariidae) were also sampled. Currently, 2240 spider species are known from South Africa (Dippenaar-Schoeman 2017), and thus, 6.1% of South African species are protected in this reserve.

Family diversity

Results from the Savanna Biome indicate that four spider families consistently dominate assemblages in terms of species richness (Foord, Dippenaar-Schoeman & Haddad 2011b; Dippenaar-Schoeman, Foord & Haddad 2013): Araneidae, Gnaphosidae, Salticidae and Thomisidae. In this study, the Salticidae (20 spp.), Thomisidae (18 spp.), Gnaphosidae (11 spp.) and Araneidae (11 spp.) were the most species-rich families (Table 4), consistent with patterns in the Savanna Biome. Nine families are represented by singletons.

Salticidae: The Salticidae are free-living spiders found on vegetation and the soil surface. They build small silk nests attached to various substrates, in which they moult, oviposit and sometimes mate, or which they occupy during periods of inactivity (Dippenaar-Schoeman & Van den Berg 2010; Dippenaar-Schoeman 2014b). During the last survey of this study, a small round densely woven silk retreat attached to grass (Figure 3e) was sampled in the TKR, housing an immature Thyene imperialis (Rossi 1846). One species has been identified as belonging to a new genus (Galina Azarkina, pers. comm.) and one was immature. The other 17 are new records for the TKR, five spp. are SAE, two spp. are NCE, while 11 spp. are more widely distributed throughout Africa (Appendix 1).

Thomisidae: Crab spiders are free-living spiders commonly found on grass, shrubs, flowers and trees, and only few species were sampled from the soil surface (Dippenaar-Schoeman & Van den Berg 2010; Dippenaar-Schoeman 2014b). Thomisids are easily dispersed by wind and most species have a wide distribution. In the TKR, 13 genera represented by 18 spp. were sampled. Of these, only four spp. are known SAE, while the rest (14 spp.) are widely distributed throughout Africa (Appendix 1).

Gnaphosidae: The gnaphosids are free-living spiders commonly found on the ground and low vegetation (Dippenaar-Schoeman & Van den Berg 2010; Dippenaar-Schoeman 2014b). One species could not be determined, five of the 11 spp. are SAE, and the rest have a wide distribution. One species, Aneplasa nigra Tucker, 1923, has a restricted distribution and is known from the Northern and Western Cape provinces only (Appendix 1).

Araneidae: The Araneidae are web-builders and produce typical orb-webs (OWB) and modified orb-webs (MOWB) (Dippenaar-Schoeman & Van den Berg 2010; Dippenaar-Schoeman 2014b). All the members of the family (11 spp.) recorded here have a wide African distribution.

Functional groups

For this study, two main guilds were recognised, namely wandering spiders (W) (97 spp.) and web-builders (WB) (39 spp.), with further subdivisions based on microhabitat and general behaviour, as observed during surveys (Appendix 1).

Wanderers: A total of 97 spp. (71.3%) are wandering spiders, with some species living on vegetation (39 spp.) and others on the ground surface (55 spp.), with an additional three species occurring regularly in both strata. The majority of ground-dwellers are free-living soil dwellers (58 spp., 42.6%), while six spp. (4.4%) live in burrows. The Salticidae (15 spp.), Gnaphosidae (11 spp.) and Lycosidae (six spp.) are the most species rich families of ground-dwellers (Appendix 1).

Most of the burrow-dwellers belong to the suborder Mygalomorphae and include the trapdoor spider species Ancylotrypa pusilla (Figure 3a), a bag-nest migid, Moggridgea peringueyi Simon, 1903, and three theraphosid baboon spider species (Figure 3f). One species of wolf spider, possibly Hogna transvaalica (Simon, 1898) (Lycosidae) (Figure 3g), also constructs burrows. These spiders use their bright red cheliceral setae to scare off predators (Webb 2013).

A species of the termite-eating spider, Ammoxenus coccineus Simon, 1893 (Ammoxenidae), was sampled from loose sand (Figure 3h). Ammoxenids are specialist termite-feeders (Petráková et al. 2015) and use the strong setae on their chelicerae to dive into the sand (Dippenaar-Schoeman, De Jager & Van den Berg 1996a; Dippenaar-Schoeman, De Jager & Van den Berg 1996b). Two species of medical importance were sampled at TKR, the violin spider Loxosceles simillima Lawrence, 1927 (Sicariidae) (Figure 3i) and the six-eyed sand spider Sicarius testaceus Purcell, 1908 (Sicariidae) (Figure 3j).

The plant wanderers sampled from the grass and tree layer are represented by 42 spp. (30.9%). The Thomisidae (16 spp.), Salticidae (eight spp.) and Oxyopidae (six spp.) were the most diverse plant-dwellers found on grasses, shrubs and trees. Three salticid species occur both on the ground and on vegetation (Appendix 1). Some interesting results have already been published regarding the presence of Peucetia viridis (Blackwall, 1858) (Figure 3k) of the family Oxyopidae, which was sampled from the unpalatable Kalahari sour grass (Bushman's Grass), Schmidtia kalahariensis. This annual grass is only available for a short period after good rains. It has an unpleasant smell and is covered with glands that produce an acidic substance. During the survey in 2008, this was the dominant grass present and it was intensively swept, but only this one species was recorded from the grass (Dippenaar-Schoeman 2005; Vasconcellos-Neto et al. 2007).

Several species were sampled from trees, including the long-spinnered bark spiders, Hersilia sericeaPocock, 1898 (Hersiliidae) (Figure 3l), and the community nest spiders, Stegodyphus dumicola Pocock, 1898 (Eresidae).

Web-dwellers: The web-dwellers are represented by 39 spp. (28.7%), with the largest number making OWB or MOWB (14 spp., 10.3%), followed by gumfoot-webs (eight spp., 5.9%), retreat-webs (eight spp., 5.9%), funnel-webs (five spp., 3.7%), sheet-webs (three spp., 2.2%) and space-webs (one sp., 0.7%).

The physical structure of the habitat plays a role in the composition of the web-dwelling fauna, as it not only provides the necessary support for anchoring webs but also increases the availability of retreat space and modification of the microclimate, which could have an effect on spiders, as well as their prey. Most of the OWB recorded belong to the Araneidae (11 spp.) (Figure 3m and n), which construct large orb-webs between trees and shrubs. Some of these species are diurnal and they are found in their webs during the day. Some orb-web builders are associated with grasslands (Araneus, Larinia, Nemoscolusand Neoscona) and are mostly nocturnal, making their orb-webs at night and resting in retreats, usually constructed in grass inflorescences, during the day. One species is a MOWB, the tropical tent-web spider (Cyrtophora citricola [Forsskål, 1775]). Several gumfoot-web spiders of the Theridiidae (eight spp.) were sampled, including two button spiders that are of medical importance, Latrodectus geometricus C.L. Koch, 1841 (Figure 3o) and L. renivulvatus Dahl, 1902.

 

Conclusion

As signatories to the Convention on Biodiversity, South Africa has an obligation to develop a strategic plan for the conservation and sustainable utilisation of its fauna and flora. Preliminary investigations into the biodiversity of the South African Arachnida highlighted the obstacles caused by a lack of baseline biodiversity and ecological information for many of the arachnid orders (Dippenaar-Schoeman 2002). With this in mind, each biodiversity survey contributes to improving our knowledge of the geographical distribution and biology of South African spider species. This survey forms part of the SANSA for the Savanna Biome, as well as the Northern Cape province, and as such represents new provincial records for 102 species. Although this article probably represents only a portion of the spider fauna present, we hope that this information will stimulate further interest and research. Established reserves, such as TKR, can make a substantial contribution towards invertebrate conservation. However, the contribution of existing reserves can only be highlighted through studies such as this.

 

Acknowledgements

The authors would like to thank the Agricultural Research Council (ARC) and the South African National Biodiversity Institute's (SANBI) Threatened Species Programme for funding the South African National Survey of Arachnida (SANSA) phase 2; Duncan MacFadyen of E. Oppenheimer & Son trust for providing permission to sample in Tswalu Kalahari Reserve and the officials of Tswalu for their friendliness and assistance; the staff of the Arachnology section of the Biosystematics Programme, ARC - Plant Protection Research, notably Connie Anderson, Sma Mathebula and Petro Marais, for their assistance with processing the material collected; Elisabeth Tybaert (wife of Rudy Jocqué), Petro Marais and Michael Stiller (ARC) for assisting during the fieldwork; and Galina Azarkina for assistance with the Salticidae identifications.

Competing interests

The authors declare that they have no financial or personal relationships that may have inappropriately influenced them in writing this article.

Authors' contributions

All the authors are team members of SANSA and contributed towards planning this national survey. They participated in field work, identifications of specimens and curation of material. A.S.D-S. and R.L. were involved in surveys, identifications and preparation of the manuscript; C.R.H. assisted with editing the manuscript; L.N.L. and R.J. assisted with field surveys; P.W. participated in field surveys and photographed all the specimens

Funding information

The first, second and fifth authors acknowledge financial support from the National Research Foundation of South Africa.

 

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Correspondence:
Charles Haddad
haddadcr@ufs.ac.za

Received: 08 Aug. 2017
Accepted: 09 Apr. 2018
Published: 09 July 2018

 

 

Appendix 1

 

Table 1-A1 - Click to enlarge