Comparative utilisation of exotic and native <i>Solanum </i>(Solanaceae) species by <i>Chnootriba hirta</i> (Thunberg) (Coccinelidae), a native herbivorous ladybird

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Chnootriba hirta (Thunberg) feeds on the foliage of several native Solanum species in South Africa, with occasional associations with introduced congeners. In comparing the beetle’s performance and preferences across three exotic and one native Solanum species, this study produced an unusual result. During adult and larval no-choice tests, the exotic Solanum americanum Miller proved the most suitable host plant, followed by the native S. dasyphyllum Schumacher and Thonning, with the exotic cultivated S. lycopersicum Linnaeus (tomato) proving marginally suitable. In contrast, the exotic S. viarum Dunal, an invasive weed in the southern USA, did not support feeding and development. During adult choice tests, C. hirta did not discriminate between S. americanum and S. dasyphyllum, but avoided S. lycopersicum. These differences in host-plant suitability may relate, in part, to the presence of glandular leaf trichomes, renowned anti-herbivore defences, on S. viarum and S. lycopersicum, but not on S. americanum or S. dasyphyllum. Since C. hirta, a broadly oligophagous herbivore within the native Solanum insect community, cannot exploit S. viarum, the plant may well expand its range in South Africa due to an escape from insect herbivory.

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  • Cite Count Icon 2
  • 10.3897/neobiota.74.83342
An impact assessment of alien invasive plants in South Africa generally dispersed by native avian species
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  • NeoBiota
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Invasive alien plant species have been identified as a major threat to biodiversity and the relationship with native avian dispersers may increase their invasion potential. The impact of invasive plant species needs to be quantified using comparable assessment tools across different habitats and species to allocate limited resources to high-priority species. Here, we used the Generic Impact Scoring System (GISS) to assess the impacts of 16 fleshy-fruited alien invasive plant species in South Africa generally dispersed by native avian species. The results showed that fleshy-fruited invasive species have both environmental and socio-economic impacts. The cumulated impact scores for lantana (Lantana camara) and the tree of heaven (Ailanthus altissima) were the highest, with scores of 42 and 32, respectively. Some species, such as white mulberry (Morus alba), camphor tree (Cinnamomum camphora), American bramble (Rubus cuneifolius) and Brazilian pepper tree (Schinus terebinthifolius), had low overall impact scores of 8, 18, 14 and 16, respectively, but scored the maximum impact of 5 for certain mechanisms. Environmental impacts of fleshy-fruited invasive plant species had a high impact magnitude through effects on the ecosystem and vegetation. Socio-economic impacts were mainly through effects on forest production, agriculture and human health. Species with large crop sizes, small seeds and fruit sizes had higher environmental and socio-economic impact magnitude. The information generated in this study is important for guiding resource allocation and preventing the uncontrolled introduction of invasive species in South Africa. The impact of the fleshy-fruited invasive species transcended sectors and, therefore, effective management of invasive species will require the collaboration of multiple and inter-sectoral stakeholders in South Africa.

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  • Cite Count Icon 22
  • 10.1007/s10530-015-0932-1
Ingestion by an invasive parakeet species reduces germination success of invasive alien plants relative to ingestion by indigenous turaco species in South Africa
  • Jun 30, 2015
  • Biological Invasions
  • Vuyisile Thabethe + 3 more

Avian frugivores play a key role in seed dispersal of many plant species, including invasive alien plants. We assessed the effect of gut passage on the germination of selected invasive alien plant species in South Africa. Fruits of four fleshly-fruited invasive alien plant species: Solanum mauritianum, Cinnamomum camphora, Psidium guajava, and Morus alba, were fed to two species of indigenous turacos, Knysna (Tauraco corythaix) and purple-crested (Gallirex porphyreolophus) turacos, and to invasive rose-ringed parakeets (Psittacula krameri). Seed retention time was determined as this can influence both seed dispersal and germination success. Germination success of ingested seeds was compared with that of manually de-pulped seeds, as well as to seeds in whole fruit. The germination success of seeds of all the invasive plant species increased significantly after ingestion by both turaco species compared with seeds from whole fruits. Germination success of manually de-pulped seeds did not differ significantly from that of turaco ingested seeds. In contrast, seed passage through the digestive tract of rose-ringed parakeets significantly reduced germination success and viability of ingested invasive plant species. Our results suggest that Knysna and purple-crested turacos are legitimate seed dispersers of fleshy-fruited invasive plants, while rose-ringed parakeets are mainly seed predators. Although seed predation by rose-ringed parakeets negatively affects the reproductive success of these plants, it is unlikely that this will suppress the spread of these invasive alien plants in South Africa as they are already well established. Furthermore, they can facilitate dispersal by seed regurgitation and dropping uneaten fruits away from the parent plant. Similar trends could be expected for indigenous seeds that rose-ringed parakeets feed on and therefore these birds remain a negative influence within invaded ecosystems.

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  • Book Chapter
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From an economic point of view, agriculture and tourism, along with mining production, are South Africa’s largest economic sectors. However, South Africa is becoming increasingly reliant on ecotourism as an economic growth sector, which is, in turn, reliant on maintaining the productive and aesthetic value of South Africa’s protected areas and interstitial landscapes. This, together with other important human bene¢ts gained from maintaining biodiversity (e.g., ecological services, harvesting of wild species, aesthetically and culturally), suggests that key role players responsible for policy making in the country are faced with particular challenges where conservation and economic development needs are in con®ict (see e.g., reference1). Yet, at the same time, vertebrate introductions that result in invasions have the potential to alter these valuable environments. For example, considering the anthropogenic movement of ungulate species (both alien and extralimital) in South Africa, known for their recreation and food source value, Spear and Chown2 have shown that their movement has led to a 1.34% increase in the similarity of ungulate assemblages at a quarter-degree grid-cell resolution. At least 21 invasive ¢sh species are present in South Africa. While the impact of these species on aquatic ecosystems has been profound, resulting in the extirpation or localized extinction of a number of indigenous ¢shes, amphibians, and invertebrates, alien invasive ¢shes drive a large recreational ¢shery that has signi¢cant economic value. As a result of these positive economic contributions of certain invasive vertebrates, the implementation of legislation governing the importation and movement of both alien and extralimital species in South Africa will require careful consideration of the trade-offs between economic gain and biodiversity loss.

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  • Research Article
  • Cite Count Icon 40
  • 10.3897/neobiota.39.23135
Even well-studied groups of alien species might be poorly inventoried: Australian Acacia species in South Africa as a case study
  • Jun 26, 2018
  • NeoBiota
  • Nkoliso Magona + 4 more

Understanding the status and extent of spread of alien plants is crucial for effective management. We explore this issue using Australian Acacia species (wattles) in South Africa (a global hotspot for wattle introductions and tree invasions). The last detailed inventory of wattles in South Africa was based on data collated forty years ago. This paper aimed to determine: 1) how many Australian Acacia species have been introduced to South Africa; 2) which species are still present; and 3) the status of naturalised taxa that might be viable targets for eradication. All herbaria in South Africa with specimens of introduced Australian Acacia species were visited and locality records were compared with records from literature sources, various databases, and expert knowledge. For taxa not already known to be widespread invaders, field surveys were conducted to determine whether plants are still present, and detailed surveys were undertaken of all naturalised populations. To confirm the putative identities of the naturalised taxa, we also sequenced one nuclear and one chloroplast gene. We found evidence that 141 Australian Acacia species have been introduced to South Africa (approximately double the estimate from previous work), but we could only confirm the current presence of 33 species. Fifteen wattle species are invasive (13 are in category E and two in category D2 in the Unified Framework for Biological Invasions); five have naturalised (C3); and 13 are present but there was no evidence that they had produced reproductive offspring (B2 or C1). DNA barcoding provided strong support for only 23 taxa (including two species not previously recorded from South Africa), the current name ascribed was not supported for three species and, for a further three species, there was no voucher specimen on GenBank against which their identity could be checked. Given the omissions and errors found during this systematic re-evaluation of historical records, it is clear that analyses of the type conducted here are crucial if the status of even well-studied groups of alien taxa is to be accurately determined.

  • Research Article
  • Cite Count Icon 45
  • 10.1111/j.1439-0329.2007.00507.x
Occurrence of the wattle wilt pathogen, Ceratocystis albifundus on native South African trees
  • Oct 1, 2007
  • Forest Pathology
  • J Roux + 4 more

Summary Ceratocystis albifundus causes the disease known as wattle wilt of non‐native Acacia mearnsii trees in South Africa, Uganda and Kenya. Infection results in rapid wilt and death of susceptible trees and stem cankers on more tolerant trees. It has been suggested that C. albifundus is indigenous to southern Africa, possibly having spread from native Protea spp. to non‐native A. mearnsii and A. decurrens trees. Although C. albifundus has been collected from Protea spp., these reports are based on limited records for which only aged herbarium specimens exist. During surveys of wound‐infecting fungi on native tree species in South Africa, a fungus resembling C. albifundus was collected from Protea gaguedi, Acacia caffra, Burkea africana, Combretum molle, C. zeyheri, Faurea saligna, Ochna pulchra, Ozoroa paniculosa and Terminalia sericea. The identity of the fungus was confirmed as C. albifundus, using comparisons of DNA sequence data for the ITS and 5.8S gene of the rRNA operon. In pathogenicity trials, lesions were produced on C. molle and A. caffra, with some trees beginning to die at the termination of the experiment. This study represents the first report of C. albifundus from native tree species in South Africa and provides unequivocal evidence that the fungus occurs naturally on native Protea spp. The wide host range of C. albifundus, as well as its abundance on these indigenous hosts lends further support to the view that it is a native African pathogen.

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