Abstract
Invasive Alien Plants occur in numbers differing by orders of magnitude at subsequent invasion stages. Effective sampling and quantifying niches of rare invasive plants are quite problematic. The aim of this paper is an estimation of the influence of invasive plants frequency on the explanation of their local abundance. We attempted to achieve it through: (1) assessment of occurrence of self-regenerating invasive plants in urban woodlands, (2) comparison of Random Forest modelling results for frequent and rare species. We hypothesized that the abundance of frequent species would be explained better than that of rare ones and that both rare and frequent species share a common hierarchy of the most important determinants. We found 15 taxa in almost two thirds of 1040 plots with a total number of 1068 occurrences. There were recorded 6 taxa of high frequency–Prunus serotina, Quercus rubra, Acer negundo, Robinia pseudoacacia, Impatiens parviflora and Solidago spp.–and 9 taxa of low frequency: Acer saccharinum, Amelanchier spicata, Cornus spp., Fraxinus spp., Parthenocissus spp., Syringa vulgaris, Echinocystis lobata, Helianthus tuberosus, Reynoutria spp. Random Forest’s models’ quality grows with the number of occurrences of frequent taxa but not of the rare ones. Both frequent and rare taxa share a similar hierarchy of predictors’ importance: Land use > Tree stand > Seed source and, for frequent taxa, Forest properties as well. We conclude that there is an ‘explanation jump’ at higher species frequencies, but rare species are surprisingly similar to frequent ones in their determinant’s hierarchy, with differences conforming with their respective stages of invasion.
Highlights
Research on the invasion process is heavily impacted by the fact that in different stages–’transport’, ’introduction’, ’establishment’, and ’spread’ [1]–self-regenerating invasive alien plants (IAP) occur in numbers differing by many orders of magnitude
Between 0 and 7 IAP species were found in each sampling plots (SP)
It is possible that IAP abundance—which we adopted as a response variable in our models—is in large portion stochastic, especially among rare species; so it is unreasonable to expect that their behaviour would be explained through static models with general predictors
Summary
Research on the invasion process is heavily impacted by the fact that in different stages–’transport’, ’introduction’, ’establishment’, and ’spread’ [1]–self-regenerating invasive alien plants (IAP) occur in numbers differing by many orders of magnitude Does this pose problems in effectively sampling less frequent species, but it constitutes a serious challenge in quantifying their niche and the importance of the barriers that slow down the course of an invasion. The success of a species in that later phase is seen in the passage from surviving as individuals to self-sustaining abundant populations This transition may be accelerated or slowed down by the number of biotic or abiotic interactions [2]. Their further spread may be restricted by low availability of suitable habitats, e.g. Vaccinium mactocarpon on peatlands
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