Abstract

Summary Non‐native, invasive species can affect biological patterns and processes at multiple ecological scales. The multi‐scalar effects of invasions can influence community structure, ecosystem processes and function, and the nature and intensity of ecological interactions. Consequently, efforts to assess the spread of invasive species may benefit from a multi‐scale analytic approach. We analysed results from landscape‐ and population‐scale models for Syzygium jambos, a non‐native tree in the Luquillo Mountains of Puerto Rico, to demonstrate a multi‐scale approach that can be used to inform management decisions about invasive plants. At the landscape‐level, we used an Ecological Niche Modelling approach to predict environmentally suitable habitats for the target plant. At the population‐level, we constructed matrix projection models to determine the finite rate of population increase (λ) for S. jambos. We then extrapolated λ values to the landscape‐scale to obtain a distribution map of λ values for the Luquillo forest. The landscape analyses suggested that the most environmentally suitable habitats were those most similar to where S. jambos had already been observed. The population‐level analyses showed that four of the seven populations had λ values less than 1, indicating that they were projected to be below replacement. The λ distribution map showed that S. jambos growth was highest in areas where it was most common and lowest in areas where it was most rare. Our analyses further suggested that the importance of different drivers of invasion and the environmental variables that mediate them appear to be strongly scale‐dependent. Past disturbances seemed most important for controlling invasions at fine‐spatial scales; while abiotic environmental variables modulated coarse‐scale invasion dynamics. Synthesis and applications. We have shown that a multi‐scale analytic approach can be used to manage invasive species by simultaneously targeting susceptible life stages and rapidly growing populations in a landscape. The utility of this approach stems from an ability to: (i) map the distribution of habitats that can potentially sustain λ values above replacement; (ii) identify populations to manage or monitor during selected stages of an invasion; (iii) forecast the probability for a target species to increase above a critical threshold abundance; and (iv) set priorities for control and monitoring actions.

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