Abstract

Abstract1. Due to globalisation, trade and transport, the spread of alien species is increasing dramatically. Some alien species become ecologically harmful by threatening native biota. This can lead to irreversible changes in local biodiversity and ecosystem functioning, and, ultimately, to biotic homogenisation.2. We risk‐assessed all alien plants, animals, fungi and algae, within certain delimitations, that are known to reproduce in Norway. Mainland Norway and the Arctic archipelago of Svalbard plus Jan Mayen were treated as separate assessment areas. Assessments followed the Generic Ecological Impact Assessment of Alien Species (GEIAA) protocol, which uses a fully quantitative set of criteria.3. A total of 1,519 species were risk‐assessed, of which 1,183 were species reproducing in mainland Norway. Among these, 9% were assessed to have a severe impact, 7% high impact, 7% potentially high impact, and 49% low impact, whereas 29% had no known impact. In Svalbard, 16 alien species were reproducing, one of which with a severe impact.4. The impact assessments also covered 319 so‐called door‐knockers, that is, species that are likely to establish in Norway within 50 years, and 12 regionally alien species. Of the door‐knockers, 8% and 10% were assessed to have a severe and high impact, respectively.5. The impact category of most species was driven by negative interactions with native species, transformation of threatened ecosystems, or genetic contamination. The proportion of alien species with high or severe impact varied significantly across the different pathways of introduction, taxonomic groups, time of introduction and the environments colonised, but not across continents of origin.6. Given the large number of alien species reproducing in Norway and the preponderance of species with low impact, it is neither realistic nor necessary to eradicate all of them. Our results can guide management authorities in two ways. First, the use of quantitative assessment criteria facilitates the prioritisation of management resources across species. Second, the background information collected for each species, such as introduction pathways, area of occupancy and ecosystems affected, helps designing appropriate management measures.

Highlights

  • The spread of alien species as a result of human activities is a global problem with massive ecological consequences (Kumschick et al, 2015), identified as one of the five major direct drivers of global change (Intergovernmental Science–Policy Platform on Biodiversity and Ecosystem Services [IPBES], 2019)

  • Alien species in Norway were risk-assessed using Generic Ecological Impact Assessment of Alien Species (GEIAA). This method has been described in detail elsewhere (Sandvik et al, 2019b), but we present a list of the nine criteria in Table 1 and give a short overview of the method in Appendix A in the Supporting Information

  • A total of 3,104 species were considered for impact assessment

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Summary

Introduction

The spread of alien species as a result of human activities is a global problem with massive ecological consequences (Kumschick et al, 2015), identified as one of the five major direct drivers of global change (Intergovernmental Science–Policy Platform on Biodiversity and Ecosystem Services [IPBES], 2019). Through the Convention on Biological Diversity (CBD), many governments have committed to “Prevent[ing] the introduction of, control[ling] or eradicat[ing] those alien species which threaten ecosystems, habitats or species” (United Nations [UN], 1992, Article 8 [h]). This goal is reinforced by, for example, the Aichi Target 9 (CBD, 2010, Article 13) and the European Union (EU, 2014, Article 1; see Roy et al, 2018). These international obligations are followed up in national legislation, for example, in Norway’s aim “to prevent the import, release and spread of alien organisms that have or may have adverse impacts on biological or landscape diversity” (KLD [The Royal Norwegian Ministry of Climate and Environment], 2015a, §1)

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