Dickson’s Strandveld Copper, Chrysoritis dicksoni (Gabriel, 1947) was discovered in September 1946 by Charles Dickson near Melkboschstrand. It has always been a scarce butterfly, and has had a history of disappearing from its known habitats and then being rediscovered. Its original known strongholds were in the area between Melkboschstrand and Mamre on the Cape West coast. These colonies were lost one by one through expansion of agricultural activities and encroachment of alien vegetation. The last area where it occurred on the west coast was near the Pella mission station, where it had eight sub populations over an area of 60 ha. These colonies also died out and by the mid-1990s it was effectively extinct on the west coast. A population that had been found near Witsand on the south Cape coast in 1979 also disappeared. However, persistent searches by Ernest Pringle led to the discovery of more localities further inland. The butterfly is holding on at these sites, but is severely threatened by alien plant invasions at one site.
IUCN RED-LIST STATUS
Originally Red-Listed as VULNERABLE (Henning & Henning, 1989), it was upgraded to CRITICALLY ENDANGERED in the latest revision of the Red List, following the loss of the west coast populations (Henning et al., 2009), and this status was confirmed in the South African Butterfly Atlas (Mecenero et al., 2013), and the South African Lepidoptera Conservation Assessment project (Mecenero et al., 2015).
CURRENT SCIENTIFIC KNOWLEDGE
Melkboschstrand, Western Cape.
There are two main, disjunct population groups. One group was found on the West Coast between Melkbosstrand and Atlantis (three colonies, now all apparently ‘extinct’). The other population group occurs near Witsand (at the mouth of the Breede River). The West Coast populations fluctuated in numbers significantly from year to year before their eventual extinction (Heath & Brinkman 1995). The Witsand populations have remained strong since their discovery by the Pringles, and recent research has shown that they are spread over an area of some 10 hectares (Giliomee & Edge, 2015; Edge, 2016).
Clark & Dickson (1971) described the habitats north of Cape Town as a sandveld type, with short vegetation. Near Atlantis, the species was found in Atlantis Sand Fynbos (Mucina & Rutherford 2006), with the dominant plants being peperbos, Montinia caryophyllacea Thunb. (Montiniaceae), and dakriet (Restionaceae) amongst which the associated ant built its nests (Henning et al. 2009).
The habitat north of Witsand was found by Edge (2016) to be mainly Canca Limestone Fynbos (Mucina & Rutherford 2006), with the dominant plants being Passerina galpinii C.H. Wright, Pentameris calcicola (H.P. Linder) Galley, Thamnocortus pluristachyus Mast., Phylica ericoides L., and Searsia glauca (Thunb.) Moffett. The third and fifth plant species listed are frequently utilised by the host ants Crematogaster peringueyi Emery to build their carton nests. The butterfly and the ant species appear to be particularly sensitive to disturbance, and colonies move their exact location every few years
Adults fly from around mid-August towards the latter part of September.
Male territorial behaviour
Adult males are decidedly gregarious and congregate at certain spots in open sandy areas (similar to ‘lek’ behaviour in moths) (Clark & Dickson 1971, Curle & Ficq 2009). When disturbed they fly low in circles, often settling again on low vegetation or on the ground, returning sometimes to the same perch.
Mating takes place when a female enters the ‘lek’ area and after a contest between the males present the victor mates with the female. Mating has also been observed taking place straight after emergence when a male and female hatch close after each other, on top of the ants’ carton nest (Giliomee & Edge, 2015). Coupling lasted for about twenty minutes and the ants did not attack the pair.
Female oviposition behaviour
Females fly randomly about the habitat, and are sometimes encountered far away from known breeding sites. They oviposit on many different plants and substrates (Edge & Terblanche, 2010; Edge, 2016), and this is strong evidence of their aphytophagy.
Clark & Dickson (1971) described the egg and first instar larva, which died fairly soon after hatching. Alan Heath and his co-workers conducted much field research as well as captive rearing experiments with this species (Heath & Brinkman 1995; Heath 1998; Heath & Claassens 2000, 2003; Heath et al. 2008; Heath 2014). The larvae were found to be aphytophagous (do not feed on plants at all), and to be associated with ants (Crematogaster peringueyi) and Homopterans (aphid-like insects). The larvae are fed by ant regurgitations (trophallaxis). Heath & Brinkman (1995) described aspects of the population dynamics of Chrysoritis dicksoni based on their collections and observations in the field. They hypothesised that individuals could remain in the larval or pupal state for more than one year, if conditions were not favourable.
Originally allocated to genus Phasis Hübner, 1819, but after investigation of its morphology and life history it was transferred to the monotypic genus Oxychaeta by Tite & Dickson (1973). Heath (1997), in a revision of the tribe Aphnaeini, synonymised Oxychaeta with Chrysoritis Butler, 1898 on morphological grounds, a treatment that was later supported by DNA analysis (Rand et al. 2000).
Correct vegetation composition and structure is essential to promote the right conditions (microclimate) for the host ants and the scale insects which suck sap from certain plant species. Fire is not usually an ecosystem driver in this vegetation type, with its low biomass per m2, and predominance of succulent or fire resistant plants. This can be altered drastically by dominance of alien plants. Grazing and browsing of a healthy community of animals is the main ecosystem driver promoting the correct vegetation.
Threats to existing populations
Increasing alien vegetation will make fires more likely, threatening the ants’ carton nests which are above ground and quite flammable. Overgrazing by domestic animals such as cattle, sheep and ostriches can alter the vegetation composition and structure and the microclimate. It is quite likely that the extinction of the species on the West coast north of Cape Town was accelerated by climate change, making populations smaller and more isolated. This would lead to loss of genetic heterogeneity and further reduce the ability to adapt.
Research on the butterfly’s life history and ecological requirements is continuing and includes study of:
- Adult butterfly behaviour and habitat requirements
- Female butterfly oviposition (egg laying) behaviour
- Observations of the larval stages of the butterfly, including its association with ants and Homopterans.
- The preferred microclimate conditions necessary for the butterfly and its early stages and associates.
- Sampling and identification of ant species assemblages and Homopteran populations at the places where the butterfly occurs.
- The population of the butterfly at its various locations.
The remaining known populations occur on two privately owned farms north of Witsand, spread over an area of c. 20 ha. One of the farms is well managed, with good control of alien vegetation and moderate levels of grazing, and as long as this regime prevails the butterfly should be safe. The other farm, owned by Stellenbosch University (SU), was historically overgrazed by tenant farmers and was heavily infested with alien vegetation (mainly Rooikrans Acacia cyclops). Prior to intervention the butterfly’s populations were shrinking. Negotiations with the tenant farmer and CapeNature led to the cessation of grazing and an aggressive alien removal programme, partly funded by the Brenton Blue Trust. CapeNature and SU are negotiating a stewardship agreement for the land occupied by C. dicksoni, after which it will be managed by sound ecological principles to benefit the butterfly and the ecosystem which sustains it.
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Curle, A.I. & Ficq, H.C. 2009. The plot thickens – Chrysoritis dicksoni (Gabriel, 1947): some recent field observations. Metamorphosis 20(4): 108–114.
Edge, D.A. 2005. Butterfly conservation in the southern Cape. Metamorphosis, 16(2): 28–46.
Edge, D.A. 2016. Vegetation associated with the critically endangered butterfly Chrysoritis dicksoni (Gabriel, 1947) (Lepidoptera: Lycaenidae: Aphnaeinae) at Witsand, Western Cape Province. Metamorphosis 27: 66–77.
Edge, D.A. & Giliomee, J. 2015. The ants and scale insects on which the critically endangered butterfly Chrysoritis dicksoni (Gabriel) (Lepidoptera: Lycaenidae: Aphnaeinae) depends for its survival. Metamorphosis 26: 38–43.
Edge, D.A. & Terblanche, R.F. 2010. Research into the life history and ecology of Chrysoritis dicksoni (Gabriel) (Lepidoptera: Lycaenidae). Metamorphosis 21(3): 120–127.
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Heath, A. & Brinkman, A.J. 1995. Aspects of the life history, distribution and population fluctuations of Oxychaeta dicksoni (Gabriel) (Lepidoptera: Lycaenidae). Metamorphosis 6(3): 117–127.
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Mecenero, S., Edge, D.A. & Staude, H.S. 2015. Southern African Lepidoptera Conservation Assessment (SALCA). Metamorphosis 26: 116–122.
Rand, D.B., Heath, A., Suderman, T. & Pierce, N.E. 2000. Phylogeny and life history evolution of the genus Chrysoritis within the Aphnaeini (Lepidoptera: Lycaenidae), inferred from mitochondrial Cytochrome oxidase I sequences. Molecular Phylogenetics and evolution 17: 85–96.
Tite, G.E. & Dickson, C.G.C. 1973. The genus Aloeides and allied genera (Lepidoptera: Lycaenidae). Bulletin of the British Museum of Natural History (Entomology) 29: 225–280.