Species‐ and site‐specific impacts of an invasive herbivore on tree survival in mixed forests

Abstract

Invasive herbivores are often managed to limit their negative impact on plant populations, but herbivore density – plant damage relationships are notoriously spatially and temporally variable. Site and species characteristics (both plant and herbivore) must be considered when assessing the potential for herbivore damage, making it difficult to set thresholds for efficient management. Using the invasive brushtail possum Trichosurus vulpecula in New Zealand as a case study, we parameterized a generic model to predict annual probability of browse‐induced mortality of five tree species at 12 sites. We compared predicted and observed tree mortality for each species + site combination to establish herbivore abundance – tree mortality thresholds for each site on a single and combined tree species basis. Model results indicated it is likely that possum browse was the primary cause of all tree mortality at nine of the 12 species‐site combinations, allowing us to estimate site‐specific thresholds below which possum population numbers should be reduced and maintained to keep tree mortality under a predetermined level, for example 0.5% per year. The browse model can be used to set site‐ and species‐specific management action thresholds, and can be adapted easily for other plant or herbivore species. Results for multiple plant or herbivore species at a single site can be combined to create conservative, site‐wide management strategies, and used to: determine which sites will be affected most by changes in herbivore abundance; quantify thresholds for herbivore management; and justify expenditure on herbivore control.

Past, present and two potential futures for managing New Zealand’s mammalian pests

“…It requires some understanding of the pest-asset relationship and how it may change in time and space so that target densities or conditions can be set for either the pests or assets, especially when the relationships are non-linear (Nugent et al 2001;Norbury et al 2015), vary between sites (Holland et al 2016), or are affected by extrinsic events such as rainfall (Choquenot & Parkes 2001). Setting target densities for pests allows planned intervention to be applied depending on the initial population reduction and the rate at which the target population recovers (Choquenot & Parkes 2001).…”

Eradicating an invasive mammal requires local elimination and reduced reinvasion from an urban source population

“…Possum impacts on New Zealand ecosystems are well documented. As folivores they consume millions of tonnes of vegetation annually (Russell et al, 2015), causing canopy die‐back and changes in community composition (Gormley et al, 2012; Holland et al, 2016; Nugent et al, 2010). As opportunistic omnivores they prey on and compete with native birds and invertebrates (Clout, 2006; Sadlier, 2000).…”