scholarly journals Biotic Interactions as Mediators of Biological Invasions: Insights from South Africa

Author(s):  
Johannes J. Le Roux ◽  
Susana Clusella-Trullas ◽  
Thabiso M. Mokotjomela ◽  
Mario Mairal ◽  
David M. Richardson ◽  
...  
Author(s):  
John R. Wilson ◽  
John Measey ◽  
David M. Richardson ◽  
Brian W. van Wilgen ◽  
Tsungai A. Zengeya

Author(s):  
Brian W. van Wilgen ◽  
Tsungai A. Zengeya ◽  
David M. Richardson

Author(s):  
Thabiso M. Mokotjomela ◽  
Tshamaano Nemurangoni ◽  
Tsedzuluso Mundalamo ◽  
Thulisile P. Jaca ◽  
Anesu G. Kuhudzai

Author(s):  
Tendamudzimu Munyai

In November 2018, South Africa published the first National Status Report on Biological Invasions and Their Management (SANBI and CIB 2018). This report represents a milestone for the Republic of South Africa and the world since it is believed to be the first comprehensive national-scale assessment for biological invasions. Moreover, the report is a formal mechanism to increase the connectivity between research, policy, and implementation, and it will be followed by assessments every three years. Data used in the report originated from a range of data sources, including formal and grey data repositories, atlas data, published scientific papers, theses, inputs from experts and practitioners, and management records from government agencies and Non-Governmental Organizations (NGOs). Several important data gaps were identified during data collection and analysis. These data gaps are largely due to a lack of a central data repository, inconsistent species checklists, data transparency, and data interoperability (due in part to a lack of consistent definitions, taxonomic classification, and use of varying data standards). To address these data gaps, the team identified several forms of databases and requested access to the data. The data received required that the team perform a preliminary validation for metadata and data completeness. Parallel to the process of sourcing and validating the data, the team compiled three comprehensive national alien and invasive species checklists, which were then verified and validated by taxonomists. These processes were followed by adopting and developing metrics to prepare data for analyses. The team identified, notwithstanding the numerous data classification schemes available, A Proposed Unified Framework for Biological Invasions (Blackburn et al. 2011), and the Environmental Impact Classification for Alien Taxa (EICAT) Scheme (Hawkins et al. 2015). These two classifications were used to assess the status of species introduction and impact, respectively. Other metrics that were developed include the confidence level metrics to assign the validated data to the indicators and criteria for reviewing area-based invasive species management plans. Finally, the data were used to assess four aspects of the report: pathways of introduction; status of alien species; status of invaded areas; and effectiveness of control measures and regulations. A total of 21 indicators were developed to assess the status of these aspects. In addition, four high-level indicators (one for each aspect) were developed for use in the national suite of environmental indicators on which the Department of Environmental Affairs reports on a regular basis. The next steps include communicating and interpreting the indicators as part of the final report; developing monitoring and reporting systems in an attempt to fill the data gaps; testing and refining the indicators with stakeholders; continuously validating and verifying the alien and invasive species checklists with a wider network of country experts; and building simulation models to assess the inter-relationship and value of indicators.


NeoBiota ◽  
2020 ◽  
Vol 62 ◽  
pp. 463-487
Author(s):  
Tamara B. Robinson ◽  
Nicole Martin ◽  
Tainã G. Loureiro ◽  
Phikolomzi Matikinca ◽  
Mark P. Robertson

The implications of climate change for biological invasions are multifaceted and vary along the invasion process. Changes in vectors and pathways are likely to manifest in changes in transport routes and destinations, together with altered transit times and traffic volume. Ultimately, changes in the nature of why, how, and where biota are transported and introduced will pose biosecurity challenges. These challenges will require increased human and institutional capacity, as well as proactive responses such as improved early detection, adaptation of present protocols and innovative legal instruments. Invasion success and spread are expected to be moderated by the physiological response of alien and native biota to environmental changes and the ensuing changes in biotic interactions. These in turn will likely affect management actions aimed at eradicating, containing, and mitigating invasions, necessitating an adaptive approach to management that is sensitive to potentially unanticipated outcomes.


Bothalia ◽  
2017 ◽  
Vol 47 (2) ◽  
Author(s):  
Costas Zachariades ◽  
Iain D. Paterson ◽  
Lorraine W. Strathie ◽  
Martin P. Hill ◽  
Brian W. Van Wilgen

Background: Biological control of invasive alien plants (IAPs) using introduced natural enemies contributes significantly to sustained, cost-effective management of natural resources in South Africa. The status of, and prospects for, biological control is therefore integral to National Status Reports (NSRs) on Biological Invasions, the first of which is due in 2017. Objectives: Our aim was to evaluate the status of, and prospects for, biological control of IAPs in South Africa. We discuss expansion of biological control and suggest indicators to be used in the upcoming NSR to assess sufficient growth. Method: We used published literature, unpublished work and personal communication to assess the status of biological control of IAPs. We propose indicators based on the targets for biological control that were proposed in the 2014 ‘National Strategy for dealing with biological invasions in South Africa’. To prioritise targets for future efforts, we used published lists of damaging IAPs and assessed the prospects for their biological control. Recommendations for using biological control as a management tool were made after discussion among the authors and with colleagues. Results: Significant control of several Cactaceae, Australian Acacia species and floating aquatic plants, and many other IAPs has been achieved in South Africa since 1913. Recently, biological control has benefited from improved international collaboration, a streamlined application process for the release of new biological control agents (resulting in the approval of 19 agents against 13 IAP species since 2013), and increased funding and capacity. There is still a need to improve implementation and to better integrate biological control with other control methods. In order to maximise benefits from biological control, increased investment is required, particularly in implementation and post-release evaluation, and in targeting new IAPs. Proposed targets for growth between 2017 and 2020 include an increase in financial investment in research by 29%, implementation by 28% and mass-rearing by 68%. Research capacity should increase by 29%, implementation capacity by 63% and mass-rearing capacity by 61%. New research projects should be initiated on 12 new IAP targets, while post-release monitoring efforts should be expanded to another 31 IAPs. Conclusion: Biological control of IAPs has contributed substantially to their management in South Africa, and continues to do so. Further investment in targeted aspects of IAP biological control will increase this contribution.


Bothalia ◽  
2001 ◽  
Vol 31 (1) ◽  
pp. 99-115 ◽  
Author(s):  
S. D. J. Privett ◽  
R. M. Cowling ◽  
H. C. Taylor

This study used permanently marked 50 m: sites, surveyed at a 30 year interval, to provide a descriptive account of the temporal change in the fynbos vegetation of the Cape of Good Hope Nature Reserve. South Africa. Management records were used to examine the role of post-fire age. fire frequency and intensity, as well as biotic interactions (competition from overstorey proteoids and alien plants) in influencing vegetation composition over this time period. The mean similarity in species composition of sites between surveys was 62%, indicating an average of nearly 40% turnover in species over the 30 year period. The main causes of this change included differences resulting from different stages in the post-fire succession as well as the impact of differential fire regimes (especially frequency effects). Competition from serotinous Proteaceae. which proved highly mobile after fire, as well as invasive Australian acacias also impacted on the composition of the vegetation over time. The study demonstrated that fynbos communities are temporally dynamic and that the changes over time in species composition are caused by a variety of processes. The study also provided evidence for the role of temporal diversity in contributing to the high species diversity in fynbos systems.


2020 ◽  
Vol 16 (11) ◽  
pp. 20200651
Author(s):  
James Baxter-Gilbert ◽  
Julia L. Riley ◽  
Carla Wagener ◽  
Nitya P. Mohanty ◽  
John Measey

Island ecosystems have traditionally been hailed as natural laboratories for examining phenotypic change, including dramatic shifts in body size. Similarly, biological invasions can drive rapid localized adaptations within modern timeframes. Here, we compare the morphology of two invasive guttural toad ( Sclerophrys gutturalis ) populations in Mauritius and Réunion with their source population from South Africa. We found that female toads on both islands were significantly smaller than mainland counterparts (33.9% and 25.9% reduction, respectively), as were males in Mauritius (22.4%). We also discovered a significant reduction in the relative hindlimb length of both sexes, on both islands, compared with mainland toads (ranging from 3.4 to 9.0%). If our findings are a result of natural selection, then this would suggest that the dramatic reshaping of an amphibian's morphology—leading to insular dwarfism—can result in less than 100 years; however, further research is required to elucidate the mechanism driving this change (e.g. heritable adaptation, phenotypic plasticity, or an interaction between them).


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