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Informing eradication feasibility: ecological context and delimitation for boneseed (Chrysanthemoides monilifera subsp. monilifera) in Western Australia

2024/09/01 by Kathryn L. Batchelor, J. K. Scott, Bruce L. Webber · 1 voice
Agricultural and Biological Sciences · Environmental Science · #Animal Ecology and Behavior Studies #Biological Control of Invasive Species #Wildlife Ecology and Conservation

paper · pdf · doi:10.1017/inp.2024.18

openalex publication_date 2024/09/01 · openalex created_date 2025/10/10 · openalex updated_date 2026/07/22

Abstract

Abstract The southern African shrub boneseed [ Chrysanthemoides monilifera subsp. monilifera (L.) Norl.] is a perennial shrub that is a significant threat to natural ecosystems and is listed as a Weed of National Significance in Australia. In Western Australia (WA) it has spread across peri-urban and natural environments. We assembled a single standardized database containing more than 2,050 presence records for individual plants and 135 absence records at a local population level. We further refined the populations into 89 sites that require different management trajectories due to topography and capacity of land managers to implement control. Forty-nine of these sites were in urban regions and 40 sites were in regional WA. We split these 89 sites into three near-term management goals: watch (12), extirpate (68), and contain (9). The 12 watch sites are those where all available evidence suggests that there have been no new inputs into the seedbank for 15 yr. The 68 sites marked for extirpation are those where delimitation is already achieved or easily achievable, where there have been minimal seed inputs into the soil seedbank in recent years due to consistent surveillance and control, and where surveys for new plants are likely to be efficient to conduct. Finally, for nine sites in urban regions around Perth, we recommend containment in the near term with a longer-term goal to achieve delimitation and extirpation. To achieve the objective of state-level eradication, a coordinated and sustained campaign involving three components—delimitation of all sites, prevention of further inputs into the soil seedbank, and systematic field surveys to remove plants—must commence without delay. While resourcing requirements for delimitation and overall program management are not possible to estimate, our prior experience suggests that it will take at least 1,900 h of on-ground surveying by experienced personnel to achieve extirpation of C. monilifera subsp. monilifera in WA.

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