the funds available, the costs of management, and many other factors that are not
addressed in most risk analyses. Risk analyses are also not equivalent to, and cannot
replace, management plans. While risk analyses compile much useful information
for the management of a species, pathway, or area, additional information is needed
and SMART (Specific, Measurable, Achievable, Realistic, and Timely) goals need
to be set for management. Furthermore, as mentioned earlier, desktop-based risk
analyses cannot replace detailed assessments of the feasibility of eradication
(e.g. Kaplan et al. 2012; Jacobs et al. 2014), but they can provide useful information
to aid prioritisation of potential eradication targets. South Africa has historically
taken a pragmatic or reactive approach to the issue, but we believe that the solutions
provided here offer an opportunity for more transparent and evidence-based decision-making.
Acknowledgements We thank Reuben Keller for his work on approaches to risk assessments,
Kim Canavan for advice with biological control risk assessments, and Craig Whittington-Jones for a
report on provincial processes related to import applications. We also thank the reviewers for
helpful comments. The South African Department of Environment, Forestry, and Fisheries (DEFF)
are thanked for funding the South African National Biodiversity Institute noting that this publication does not necessarily represent the views or opinions of DEFF or its employees.
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