Although research on human-mediated exchanges of species has substantially intensified during the last centuries, we know surprisingly little about temporal dynamics of alien species accumulations across regions and taxa. Using a novel database of 45,813 first records of 16,926 established alien species, we show that the annual rate of first records worldwide has increased during the last 200 years, with 37% of all first records reported most recently (1970–2014). Inter-continental and inter-taxonomic variation can be largely attributed to the diaspora of European settlers in the nineteenth century and to the acceleration in trade in the twentieth century. For all taxonomic groups, the increase in numbers of alien species does not show any sign of saturation and most taxa even show increases in the rate of first records over time. This highlights that past efforts to mitigate invasions have not been effective enough to keep up with increasing globalization.

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Human-mediated transport beyond biogeographic barriers has led to the introduction and 73The transport of species across biogeographic barriers by humans is a key component of 74 global environmental change [1][2][3] . Some of the species introduced to new regions will establish 75 self-sustaining populations and, thus, become a persistent part of the local biota 95We expect regions with higher gross domestic product per capita (GDPpc) or with higher 96 population densities to receive more alien species introductions across taxa (i.e., to experience 97 higher colonisation pressure through trade and transport), resulting in higher EAS richness 7,8,10,21 . 98We also test whether EAS richness patterns follow the latitudinal gradients often observed for 99 native biota, with higher richness in regions with higher mean annual temperature and 100 precipitation 22,23 . We expect island regions to have higher EAS richness than mainland regions, 101as islands are thought to be more prone to the establishment of alien species 12,24,25 . In addition, 102we expect more isolated oceanic islands to have greater EAS richness, as they have been shown 103 to receive more introductions, at least for birds 9 . We also expect coastal regions (as points of human population density, with a weak trend of higher alien richness in wetter regions (Table 1). 125While we only have potential proxy data (GDPpc, population density) for colonisation pressure 126 here (i.e., the total numbers of species introduced) 26 , our results suggest that cumulative numbers 127 7 of EAS are driven to a greater extent by differences in area and the pressure of introductions 128 from human history and activity 1,3,5,12,21 than by climate. 129Island regions have on average higher cross-taxon EAS richness (mean ± 1 S.D. 130proportional cross-taxon richness = 0.17 ± 0.11) than mainland regions (mean ± 1 S.D. = 0.11 ± 131 0.07; Table 1). In addition, models explaining alien richness of island and mainland regions 132 separately reveal that EAS richness is more strongly related to area, GDPpc and population 133 density on islands than in mainland regions (Table 1) (Table 1). Among mainland regions, EAS richness is greater for coastal (mean ± 1 S.D. 139proportional cross-taxon richness = 0.13 ± 0.09) than for landlocked regions (mean ± 1 S.D. = 140 0.10 ± 0.04). Cross-taxon EAS richness on islands tends to be higher for those further from 141 continental landmasses (Table 1). 143 Taxonomic congruence 144The strongest correlations in alien richness between taxonomic groups exist for ants and 145 reptiles (r s = 0.62), followed by birds and mammals, and vascular plants and spiders (both r s = 146 0.55) ( Table 2). For ants and reptiles, EAS richness is high in the Hawaiian Islands, southern 147United States (especially Florida) and Madagascar and the Mascarene Islands (Fig. 1b, 1g). (Fig. 1f, 1h). In Europe, the United Kingdom has the highest established alien 154 plant richness, while Germany has the highest spider richness (Fig. 1h, 1h). Overa...

Our ability to predict the identity of future invasive alien species is largely based upon knowledge of prior invasion history. Emerging alien species-those never encountered as aliens before-therefore pose a significant challenge to biosecurity interventions worldwide. Understanding their temporal trends, origins, and the drivers of their spread is pivotal to improving prevention and risk assessment tools. Here, we use a database of 45,984 first records of 16,019 established alien species to investigate the temporal dynamics of occurrences of emerging alien species worldwide. Even after many centuries of invasions the rate of emergence of new alien species is still high: One-quarter of first records during 2000-2005 were of species that had not been previously recorded anywhere as alien, though with large variation across taxa. Model results show that the high proportion of emerging alien species cannot be solely explained by increases in well-known drivers such as the amount of imported commodities from historically important source regions. Instead, these dynamics reflect the incorporation of new regions into the pool of potential alien species, likely as a consequence of expanding trade networks and environmental change. This process compensates for the depletion of the historically important source species pool through successive invasions. We estimate that 1-16% of all species on Earth, depending on the taxonomic group, qualify as potential alien species. These results suggest that there remains a high proportion of emerging alien species we have yet to encounter, with future impacts that are difficult to predict.

It has been argued that globalization in human-mediated dispersal of species breaks down biogeographic boundaries, yet empirical tests are still missing. We used data on native and alien ranges of terrestrial gastropods to analyze dissimilarities in species composition among 56 globally distributed regions. We found that native ranges confirm the traditional biogeographic realms, reflecting natural dispersal limitations. However, the distributions of gastropods after human transport are primarily explained by the prevailing climate and, to a smaller extent, by distance and trade relationships. Our findings show that human-mediated dispersal is causing a breakdown of biogeographic barriers, and that climate and to some extent socioeconomic relationships will define biogeography in an era of global change.

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Summary1. This account presents information on all aspects of the biology of Ambrosia artemisiifolia L. (Common ragweed) that are relevant to understanding its ecology. The main topics are presented within the standard framework of the Biological Flora of the British Isles: distribution, habitat, communities, responses to biotic factors, responses to environment, structure and physiology, phenology, floral and seed characters, herbivores and disease, and history, conservation, impacts and management. *Nomenclature of vascular plants follows Stace (2010) and, for non-British species, Flora Europaea.