Invasive alien species in Europe
Biological invasions by alien species can have far-reaching and often harmful effects on biological diversity and function of invaded ecosystems and cause significant losses in economic values. Alien species can act as vectors for new diseases, alter ecosystem processes, reduce biodiversity, disrupt the cultural landscape, reduce the value of land and water for human activities and cause other socioeconomic consequences for humans.
Contents
What is an alien species?
Alien species, also known as exotic, introduced or non-native species, are species, subspecies, or lower taxon occurring outside of the range they occupy naturally or could not occupy without direct or indirect introduction or care by humans. Although the majority of alien species cause no harm, some alien species spread very rapidly and can harm biological diversity, human health,and/or economic and esthetic values. These harmful species are called invasive alien species.
Alien species are introduced both intentionally and unintentionally. Intentional introductions are made when stocking fish for aquaculture or sport fishing, releasing game animals to the wild or spreading plants for horticulture and gardening. Unintentional introductions occur through the ballast water of ships, or with pathogens and microorganisms which hitch-hike on intentionally introduced species. Alien species encompass a diverse range of taxa that threaten European freshwater, brackish water, marine and terrestrial environments.
Invasive alien species impact biological diversity
Invasive alien species may have profound environmental consequences. These range from wholesale ecosystem changes e.g. colonisation of sand dunes by Acacia spp. and extinction of indigenous species e.g. threats to endemic coastal plants following expansion of Carpobrotus edulis, to more subtle ecological changes and increased biological homogeneity.
The introduction of an alien species to a new ecosystem may harm biological diversity by altering the structure and function of the ecosystem. The introduction of the freshwater mussel (Dreissena polymorpha) to lakes in Europe and North American has resulted in significant changes in the water quality of the lakes. The zebra mussel's successful competition with native clams has also lead to local extirpations of these native clams and has shifted primary production to benthic communities. The zebra mussel is a major macrofoulant of power-generating plants, and industrial and municipal water systems, which has generated enormous costs for society and businesses.
Alien species may also replace native species by competing for food and other resources or by predating on the native species. The North American Grey squirrel (Sciurus carolinensis), introduced to Italy and the United Kingdom, is able to use resources in habitats that have been affected by human use much more effectively than the native Red squirrel. This competition has resulted in a catastrophic reduction in populations of the Red squirrel, that threaten the very existence of the species.
Hybridization between alien and native species may lead to the loss of local genetic adaptations of native species. Hybridisation has occurred between alien sika deer (Cervus nippon nippon) and native red deer (Cervus elaphus) as well as between native and alien oaks (Quercus spp.) and willowherbs (Epilobium spp.) Hybridisation may introduce maladaptive genes to wild populations or result in a vigorous and invasive hybrid.
 |
 |
 |
| The zebra mussel (Dreissena polymorpha) has caused ecological and economic damage in watersheds in Europe and North American. Photo: Dan Minchin. |
The grey squirrel (Sciurus carolinensis) is a major threat to the existence of the native Red squirrel in Italy and the United Kingdom. Photo: Sandro Bertolino. |
Alien plants, like the Japanese knotweed (Fallopia japonica) may grow in enormous numbers and form dense growths that exclude native plants and animals. Photo: Peter Pyšek. |
Invasive alien species impact economy
Biological invasions have imposed huge losses on the European economy. Weeds and animal pests have had major economic impacts by causing damage to agriculture, forestry, aquaculture and other sectors. Examples of direct economic impacts include the damage caused by Japanese knotweed to flood defences and the impact of bark stripping by grey squirrels on forestry production.
The Western corn rootworm (Diabrotica virgifera), a serious pest of maize, was introduced in the 1990s into Serbia. Preliminary studies on the potential of establishment of Western corn rootworm show that this pest is likely to survive and develop wherever maize is grown in Europe and will lead to losses in crop yield.
Alien parasites such as Gyrodactylus salaris and Anguillicola crassus have led to dramatic decreases in fisheries sector incomes in several Nordic countries. The American oyster drill (Urosalpinx cinerea) is an important pest of the cultured oyster industry as it feeds preferably on oyster spat and is recorded as consuming more than half the oyster spat in certain European estuaries.
The muskrat and coypu, both introduced in the last century by the European fur industry, damage river banks through digging and have increased the risk and severity of floods in many central and southern European countries.
Notorious invasive alien weeds are of major economic significance e.g. Chenopodium ambrosioides, Paspalum distichum, Conyza canadensis, Oxalis pes-caprae. Other alien plants act as hosts of plant pathogens e.g. Bromus catharticus, which is a host for barley yellow dwarf virus and wheat stem rust.
Invasive alien species impact human health
Invasive alien species can also affect human health e.g. phytophotodermatitis through contact with Giant hogweed (Heracleum mantegazzianum) eruptive dermatitis following contact with Agave americana, poisoning of humans and livestock though consumption of toxic fruit e.g. Phytollaca americana, Solanum eleagnifolium or leptospirosis spread by the brown rat (Rattus norvegicus).
 |
| The Canada goose frequents parks and beaches in such large numbers, that its fecies can pollute water to such a degree that it may become a health hazard to swimmers and bathers. Photo: Stephen Gollasch |
Preventing the environmental impacts of invasive alien species
The number and impact of harmful invasive alien species in Europe are chronically underestimated, especially for species that do not damage agriculture or human health. Comparable estimates for Europe would play a pivotal role in informing policy and identifying resource priorities, yet to date these data are not available for any European region. Current inaction, in many though not all countries, is becoming increasingly disastrous for the region's biodiversity, health and economy.
Some impacts of past invasions could have been reduced if European countries had uniformly applied relevant rules and codes of practice and had taken rapid action to eradicate introduced species following their detection. Several biological invasions now threatening Europe might have been prevented by a higher level of awareness of IAS issues and a stronger commitment to address it.
Preventing the harmful impact of invasive species on ecosystems is a fundamental requirement of the European Biodiversity Strategy, yet in the absence of reliable regional analyses the Member States have been unable to tackle this issue strategically. Cooperative actions between Member States is particularly important within Europe, with its shared coastline, transboundary mountain ranges and protected areas and international watercourses, as species introduced into the territory of one State can easily spread to neighbouring States, subregions or the entire region. DAISIE will represent a significant element of the European commitment to international biodiversity conservation and assist member states in their obligations under Community legislation (Agenda 21).
Invasive alien species and climate change
Future global diversity scenarios highlight dramatic increases in biological invasions in European ecosystems. Further invasions will be facilitated by increased global trade and travel interacting with effects through rising atmospheric carbon dioxide concentrations, warmer temperatures, greater nitrogen deposition, altered disturbance regimes and increased habitat fragmentation.
Aquatics
Books
Gollasch S, Galil BS, Cohen AN (2006) Bridging Divides - Maritime canals as invasion corridors. Monographiae biologicae 83. Springer. 315 pp.
Research papers
Ahyong ST, Galil BS (2006) First Mediterranean record of the Indo-West Pacific mantis shrimp, Clorida albolitura Ahyong & Naiyanetr, 2000 (Stomatopoda, Squillidae). Aquatic Invasions 1(3): 191-193.
Alexandrov B, Boltachev A, Kharchenko T, Lyashenko A, Son M, Tsarenko P, Zhukinsky V (2007) Trends of aquatic alien species invasions in Ukraine. Aquatic Invasions 2(3): 215-242
Bogi C, Galil BS (2007) First record of Theora (Endopleura) lubrica Gould, 1861 (Mollusca: bivalvia: Semelidae) from a Levantine port. Aquatic Invasions 2(1): 77-79.
Galil BS (2006) A rare record of Hyastenus hilgendorfi (Crustacea: Decapoda: Majidae) from the Levant. Aquatic Invasions 1(4): 284-285.
Galil BS (2007) Loss or gain? Invasive aliens and biodiversity in the Mediterranean Sea. Mar. Poll. Bull. 55(7-9): 314-322.
Galil BS (2007) Seeing Red: Alien species along the Mediterranean coast of Israel. Aquatic Invasions 2(4): 281-312.
Galil BS, Nehring S, Panov V (2006) Waterways as invasion highways - impact of climate change and globalization. In: Nentwig, E. (Ed.) Biological invasions. Ecological Studies, vol. 193: 59-74.
Gollasch S (2006) Overview on Introduced Aquatic Species in European Navigational and Adjacent Waters. Helgol. Mar. Res. 60, 84-89
Gollasch S (2007) Marine vs. freshwater invaders - is shipping the key vector for species introductions to Europe? 339-345. In: Gherardi (ed.): Biological Invaders in inland waters: profiles, distribution and threats. Springer, Dordrecht, The Netherlands, 733 pp.
Gollasch S (2007) Is ballast water a major dispersal mechanism for marine organisms? 49-57. In: Nentwig, W. (ed.) Biological invasions. 441 pp. Ecological Studies, Vo. 193, Springer, Berlin, Heidelberg, New York
Gollasch S, Nehring S (2006) National checklist for aquatic alien species in Germany. Aquatic Invasions 1(4), 245-269
Kerckhof F, Haelters J, Gollasch S (2007): Alien species in the marine and brackish ecosystem: the situation in Belgian waters. Aquatic Invasions 2(3), 243-257
Kozhara AV, Zhulidov AV, Gollasch S, Przybylski M, Poznyak VG, Zhulidov DA, Gurtovaya TYu (2007) Dispersal and status of the bitterling Rhodeus sericeus amarus (Bloch) in Russia and adjacent countries. Folia Zoologica, 56(1): 97-108
Minchin D (2006) First Irish record of the Chinese-mitten crab Eriocheir sinensis (Milne-Edwards, 1854) (Decapoda: Crustacea). Irish Naturalists’ Journal 28(7): 303-304
Minchin D (2007a) Aquaculture and transport in a changing environment: overlap and links in the spread of alien biota. Marine Pollution Bulletin 55: 302-313.
Minchin D (2007b) Rapid coastal survey for targeted alien species associated with floating pontoons in Ireland. Aquatic Invasions 2(1): 63-70.
Minchin D (2007) A checklist of alien and cryptogenic aquatic species in Ireland. Aquatic Invasions 2(4): 341-366
Minchin D, Davis MH, Davis ME (2006) Spread of the Asian tunicate Styela clava Herdman, 1882 to the east and south-west coasts of Ireland. Aquatic Invasions 1(2): 91-96.
Minchin D, Nunn J (2006) Further range extensions of the marine gastropod Calyptraea chinensis (L.) in Ireland. Irish Naturalists’ Journal. 28 (5): 200-203.
Minchin D, Sides E (2006) Appearance of a cryptogenic tunicate, a Didemnum sp. fouling marina pontoons and leisure craft in Ireland. Aquatic Invasions 1, (3): 143-147.
Ojaveer H, Gollasch S, Jaanus A, Kotta J, Laine A, Minde A, Normant M, Panov V (2007) Chinese mitten crab Eriocheir sinensis in the Baltic Sea - supply-side invader? Biological Invasions 9: 409-418
Olenin S, Minchin D, Daunys D (2007). Assessment of biopollution in aquatic ecosystems. Marine pollution bulletin, 55 (7-9), 2007, 379-394
Özcan T, Galil BS, Bakır K, Katağan T (2006) The first record of the banana prawn Fenneropenaeus merguiensis (De Man, 1888) (Crustacea: Decapoda: Penaeidae) from the Mediterranean Sea. Aquatic Invasions 1(4): 286-288.
Panov V (2006) First record of the Chinese mitten crab, Eriocheir sinensis H. Milne Edwards, 1853 (Crustacea, Decapoda, Varunidae) from Lake Ladoga, Russia. Aquatic Invasions 1: 28-31
Panov V, Dgebuadze Y, Shiganova T, Filippov A, Minchin D (2007) A risk assessment of biological invasions: inland waterways of Europe - the northern invasion corridor case study. In: F. Gherardi (ed) Biological Invaders in Inland Waters: Profiles, Distribution and Threats. Invading Nature - Springer Series in Invasion Ecology, Vol. 2: 639-656
Panov V, Gollasch S (2006) Aquatic Invasions - the new European journal of applied research on biological invasions in aquatic ecosystems. Aquatic Invasions 1: 1-3
Panov VE, Rodionova NV, Bolshagin PV, Bychek EA (2007) Invasion biology of Ponto-Caspian onychopod cladocerans (Crustacea: Cladocera: Onychopoda). Hydrobiologia 590: 3-14
Panov VE, Yu Y, Shiganova TA, Filippov A, Minchin D (2007) Inland waterways of Europe: The northern invasion corridor case study. In: F. Gherardi: Biological Invaders in Inland waters: profits and threats Springer 639-656.
Reise K, Olenin S, Thieltges DW (2006). Editorial, Helgoland Marine Research, 60 (2):75 - 76
Rodionova N, Panov V (2006) Establishment of the Ponto-Caspian predatory cladoceran Evadne anonyx in the eastern Gulf of Finland, Baltic Sea. Aquatic Invasions 1: 7-12
Shakirova FM, Panov VE, Clark PF (2007) New records of the Chinese mitten crab, Eriocheir sinensis H. Milne Edwards, 1853, from the Volga River, Russia. Aquatic Invasions 2: 169-173
Yokes B, Galil BS (2006a) Touchdown - first record of of Percnon gibbesi (Crustacea: Decapoda: Grapsidae) along the Levant coast. Aquatic Invasions 1(3): 130-132.
Yokes B, Galil BS (2006b) The first record of the needle-spined urchin Diadema setosum (Leske, 1778) (Echinodermata: Echinoidea: Diadematidae) from the Mediterranean Sea. Aquatic Invasions 1(3): 188-190.
Yokes B, Galil BS (2006c) New records of alien decapods (Crustacea) from the Mediterranean coast of Turkey, with description of a new palaemonid species. Zoosystema 28(3): 747-755.
Zaiko A, Olenin S, Daunys D, Nalepa T (2007) Vulnerability of benthic habitats to the aquatic invasive species. Biological invasions. (Online) DOI 10.1007/s10530-006-9070-0
Zaouali A, ben Souissi J, Galil BS, d’Udekem d’Acoz C, ben Abdallah A (2007) Grapsoid crabs (Crustacea: Decapoda: Brachyura) new to the Sirte Basin, southern Mediterranean Sea - the roles of vessel traffic and climate change. JMBA2.
Fungi
Desprez-Loustau ML, Robin C, Buée M, Courtecuisse R, Garbaye J, Suffert F, Sache I, Rizzo D (2007) The fungal dimension of biological invasions. Trends Ecol Evol 22:472-480.
Desprez-Loustau ML, Robin C, Blancard D, Courtecuisse R, Husson C, Lung B, Moreau PA, Selosse MA, Sache I. Alien invasive fungi in Europe: inventory and spatio-temporal patterns with a particular focus on France. 9th International Congress of Plant Pathology, Torino, August 2008.
Invertebrates
Papers
Brown P, Adriaens T, Bathon H, Cuppen J, Goldarazena A, Hägg T, Kenis M, Klausnitzer B, Kovar I, Loomans A, Majerus M, Nedved O, Pedersen J, Rabitsch W, Roy H, Ternois V, Zakharov I, Roy D (2008) Harmonia axyridis in Europe: spread and distribution of a non-native coccinellid. BioControl, in press.
Kenis M, Rabitsch W, Auger-Rozenberg MA, Roques A (2007) How can alien species inventories and interception data help us prevent insect invasions? Bulletin of Entomological Research 97, 489-502.
Kobelt M, Nentwig W (2007)
Alien spider introductions to Europe supported by global trade.
Diversity and Distributions (OnlineEarly Articles).
doi:10.1111/j.1472-4642.2007.00426.x
Rabitsch W, Heiss E (2005) Leptoglossus occidentalis Heidemann, 1910, eine amerikanische Adventivart auch in Österreich aufgefunden (Heteroptera, Coreidae). Berichte des naturwissenschaftlich-medizinischen Verein Innsbruck 92, 131-135.
Rabitsch W., Essl, F. (2006) Biological invasions in Austria: patterns and case studies. Biological Invasions 8(2), 295-308.
Rabitsch W, Schuh R (2006) First record of the multicoloured Asian ladybird Harmonia axyridis (Pallas, 1773) in Austria. Beiträge zur Entomofaunistik 7, 161-164.
Rabitsch W (2008) The Times they are a-changin’: Driving forces of recent additions to the Heteroptera fauna of Austria. Pensoft Publishers, Sofia, in press.
Robinet C, Roques A (2008) Insect populations already impacted by climate change. Journal of Insect Science. in press
Roques A, Auger- Rozenberg MA (2006) Tentative analysis of the interceptions of nonindigenous organisms in Europe during 1995-2004. EPPO Bulletin, 36, 490-496
Roques A (2007) Old and new pathways for invasion of exotic forest insects in Europe - first results of the European project DAISIE. pp. 80-88 in Evans H. & Oszako T.(eds) “Alien Invasive Species and International Trade” Proc. IUFRO Conference S7.03.12. Forest Institute, Warzaw.
Conference presentations
Roques A (2006) European strategy for combating forest invasives. North American Forest Insects Working Conference, Asheville, North Carolina, 24-27 May 2006
Roques, A (2006) Changement global: Surveillance des espèces et invasions biologiques. Colloque Insectes et Biodiversité, Micropolis, St Léons, France, 6-7 October 2006
Roques A (2006) Invasive invertebrates in Europe: Review and current challenges. Invited lecture at International Symposium of Integrative Zoology, Beijing, 18-21 October 2006.
Roques A (2007) Invasive insect species in Europe: First results of the DAISIE and ALARM projects. 18th USDA Interagency Research Forum on Invasive Species Annapolis, Maryland, 9-12 January 2007
Roques A, Rasplus JY (2007) A review of alien invertebrates in Europe - First results of the European project DAISIE. International Conference on Alien Arthropods in South East Europe, crossroad of three continents19-21 September 2007 Sofia, Bulgaria
Roques A (2007) Invading insects species of Northeast Asia established in Europe and potential for European species to invade Northeast Asia. International Conference for Ecology and Resources of Northeast Asia, October 22-25, 2007, Beijing, China
Roques A (2007) Enseignement des travaux d'inventaire sur les insectes exotiques : du listing à la typologie des traits. Colloque « Invasions et traits d’Histoire de vie », November 14- 16, 2007, Rennes, France
Plants
Book chapters
Kühn I, Klotz S (2007). From Ecosystem invasibility to local, regional and global patterns of invasive species. In: Nentwig W (ed.), Biological invasions. Ecological Studies 193, pp.181-196, Springer-Verlag, Berlin Heidelberg.
Pyšek P, Richardson DM (2007): Traits associated with invasiveness in alien plants: Where do we stand? - In: Nentwig W (ed.), Biological invasions, Ecological Studies 193, pp. 97-125, Springer-Verlag, Berlin & Heidelberg.
Research papers
Bazos I, Kokkoris Y, Zikos A, Andriopoulos P, Delipetrou P, Georghiou K, Yannitsaros A, Arianoutsou M (2007). The alien vascular flora of Greece: floristic analysis and chorology. Bocconea (in review)
Essl F (2007). From ornamental to detrimental? The incipient invasion process of the Empress Tree (Paulownia tomentosa) in Central Europe. Preslia 79:377-389.
Essl F (2007). Verbreitung, Status und vegetationskundliches Verhalten der Strobe (Pinus strobus) in Österreich. Tuexenia 27: 59-72.
Lambdon P. W., Pyšek P., Basnou C., Hejda M., Arianoutsou M., Essl F., Jarošík V., Pergl J., Winter M., Anastasiu P., Andriopoulos P., Bazos I., Brundu G., Celesti-Grapow L., Chassot P., Delipetrou P., Josefsson M., Kark S., Klotz S., Kokkoris Y., Kühn I., Marchante H., Perglov? I., Pino J., Vila M., Zikos A., Roy D. & Hulme P. E. (2008): Alien flora of Europe: species diversity, temporal trends, geographical patterns and research needs. Preslia 80: 101-149.
La Sorte FA, McKinney ML, Pyšek P (2007): Compositional similarity among urban floras within and across continents: biogeographical consequences of human mediated biotic interchange. Global Change Biology 13: 913-921.
La Sorte F. A., McKinney M. L., Pyšek P., Klotz S., Rapson G. J., Celesti-Grapow L. & Thompson K. (2008): Distance decay of similarity among European urban floras: the impact of anthropogenic activities on b diversity. Global Ecology and Biogeography 17: 363-371.
Mihulka S, Pyšek P, Martínková J, Jarošík V (2006) Invasiveness of Oenothera congeners alien to Europe: Jack of all trades, master of invasion? - Perspectives in Plant Ecology, Evolution and Systematics 8: 83-96.
Pyšek P., Jarošík V., M?llerová J., Pergl J. & Wild J. (2008a) Comparing the rate of invasion by Heracleum mantegazzianum at the continental, regional and local scale. Diversity and Distributions 14: 355-363.
Pyšek P & Richardson DM (2006) The biogeography of naturalization in alien plants. Journal of Biogeography 33: 2040-2050.
Pyšek P., Richardson D. M., Pergl J., Jarošík V., Sixtová Z. & Weber E. (2008): Geographical and taxonomic biases in invasion ecology. Trends in Ecology and Evolution 23: 237-244.
Sádlo J, Chytrý M, Pyšek P (2007): Regional species pools of vascular plants in habitats of the Czech Republic. Preslia 79: 303-321.
Vogl G, Smolik M, Stadler LM, Leitner M, Essl F, Dullinger S, Kleinbauer I (submitted): Modelling the spread of ragweed: effects of habitat, climate change and diffusion. European Journal of Physics.
Williamson M., Dehnen-Schmutz K., Kühn I., Hill M., Klotz S., Milbau A., Stout J. & Pyšek P. (2009) The distribution of range sizes of native and alien plants in four European countries and the effects of residence time. Diversity and Distributions, doi: 10.1111/j.1472-4642.2008.00528.x
Winter M, Kühn I, Nentwig W, Klotz S (2007). Spatial aspects of trait homogenization within the German Flora. Journal of Biogeography (in review)
Conference proceedings
Arianoutsou M, Kokkoris Y, Andriopoulos P, Bazos I, Zikos A, Delipetrou P (2006). Life history traits and habitat preferences of the alien plants in Greece. In: Rokich D, Wardell-Johnson G, Yates C, Stevens J, Dixon K, McLellan R and Moss G (eds), Proceedings of the MEDECOS XI 2007 Conference, Perth, Australia. Kings Park and Botanic Garden, Perth, Australia. pp. 7-8.
Bazos I, Delipetrou P, Kokkoris I, Zikos A, Andriopoulos P, Papacharalambous E, Georghiou K, Yannitsaros A, Arianoutsou M (2006). The ecological profile of the alien flora of Greece and Cyprus: Early results. In: Book of Abstracts of the 3rd Conference of the Hellenic Ecological Society and the Hellenic Zoological Society, Ioannina, Greece. p. 37
Bazos I, Delipetrou P, Kokkoris Y, Papacharalambous I, Zikos A, Andriopoulos P, Georghiou K, Yannitsaros A, Arianoutsou M (2006). The ecological profile of the alien flora of Greece and Cyprus: Early results. In: Rabitsch W, Klingenstein F, Essl F (eds.), NEOBIOTA: From Ecology to Conservation. 4th European Conference on Biological Invasions, Vienna (Austria), 27-29 September. Book of Abstracts, p. 76.
Bazos I, Kokkoris Y, Zikos A, Andriopoulos P, Delipetrou P, Georghiou K, Yannitsaros A, Arianoutsou M (2007). The alien vascular flora of Greece: floristic analysis and chorology. In: Book of Abstracts of the XII OPTIMA Meeting, Pisa, Italy, p. 164.
Kleinbauer I, Dullinger S, Essl F, Peterseil P, Englisch T (2006). Black Locust (Robinia pseudacacia L.) in Austria: the interplay of climate, climate change and range expansion. In: Rabitsch W, Klingenstein F, Essl F (eds.), NEOBIOTA: From Ecology to Conservation. 4th European Conference on Biological Invasions, Vienna (Austria), 27-29 September. Book of Abstracts, p. 160.
Rabitsch W, Klingenstein F & Essl F (eds.) (2006). NEOBIOTA: From Ecology to Conservation. 4th European Conference on Biological Invasions, Vienna (Austria), 27-29 September. Book of Abstracts, 277 pages.
Smolik M, Stadler LM, Vogl G, Essl F, Peterseil P, Dullinger S, Kleinbauer I (2006). Monte Carlo Simulations - a tool for spread prediction of alien plant species? In: Rabitsch W, Klingenstein F, Essl F (eds.), NEOBIOTA: From Ecology to Conservation. 4th European Conference on Biological Invasions, Vienna (Austria), 27-29 September. Book of Abstracts, p. 42.
Winter M, Kuehn I, Klotz S (2005). Homogenization effects on a plant-functional scale. Annual Conference of GFOE - Landscapes, ecosystems and population dynamics, functions and conservation. In: Verhandlungen der Gesellschaft für Ökologie 35: 157.
Winter, M., Kühn I, Klotz S. (2006). Genetic homogenization at different spatial scales. In: Rabitsch W, Klingenstein F, Essl F (eds.), NEOBIOTA: From Ecology to Conservation. 4th European Conference on Biological Invasions, Vienna (Austria), 27-29 September. Book of Abstracts, p. 274.
Winter M, Kühn I, Nentwig W, Klotz S (2007). Homogenization patterns in the northern hemisphere. Annual Conference of GFOE. In: Verhandlungen der Gesellschaft für Ökologie 37: 148.
Winter M, Kühn I, Nentwig W, Klotz S (2007).Genetic homogenization within the flora of Germany. Annual Conference of GFOE. In: Verhandlungen der Gesellschaft für Ökologie 36: 324.
Conference presentations
Kokkoris Y, Andriopoulos P, Papacharalambous I, Delipetrou P, Bazos I, Kazanis D, Yannitsaros A, Georghiou K, Arianoutsou M (2005). Alien plants in Mediterranean pine forests of Greece and Cyprus: evaluation of potential invasiveness. In: MEDPINE 3: International conference on conservation, regeneration and restoration of Mediterranean pines and their ecosystems, Mediterranean Agronomic Institute of Bari (MAIB) - Valenzano (Bari), Italy.
Winter M, Kühn I, Nentwig W, Klotz S (2007). Functional homogenization within the flora of Germany. EMAPI - Ecology and Management of Alien Plant Invasions, Perth (Australia).
Winter M, Kühn I, Klotz S (2005). Homogenization effects on a plant-functional scale. EMAPI - Ecology and Management of Alien Plant Invasions, Katowice (Poland).
Winter, M, Kühn I, Klotz S (2006). Genetic homogenization at different spatial scales. Conference on "Macroecological Tools for Global Change Research", Potsdam (Germany).
Vertebrates
Daisie acknowledged
Genovesi P (2007) Limits and Potentialities of Eradication as a tool for addressing biological invasions. Pp. 385-400 in: W. Nentwig (ed) Biological invasions. Ecological studies, Vol. 193.
Gherardi F, Bertolino S, Bodon M, Casellato S, Cianfanelli S, Ferraguti M, Lori E, Mura G, Nocita A, Riccardi N, Rossetti G, Rota E, Scalera R, Zerunian S, Tricarico E (2007) Animal xenodiversity in Italian inland waters: distribution, modes of arrival, and pathways. Biological Invasions. (In print)
Genovesi P Scalera R (2007) Toward a black list of invasive alien species entering Europe through trade, and proposed responses. 40 Pp. Convention on the conservation of European wildlife and natural habitats. Standing Committee 27th meeting, Strasbourg, 26-29 November 2007. T-PVS/Inf (2007) 9
Kühn I and Klotz S (2007) From Ecosystem invasibility to local, regional and global patterns of invasive species. In Nentwig, W. (ed.), Biological invasions. Ecological Studies 193: 181-196. Berlin, Heidelberg, New York: Springer.
Shirley S. and Kark S (2006) Amassing efforts against alien invasive species in Europe. PLoS Biology 4:1311-1313.
Daisie not acknowledged
Bertolino S, Genovesi P (2007) Aquatic alien mammals introduced into Italy: impacts and control strategies. Pages 175-192 in: “Biological invaders in inland waters: profiles, distribution, and threats” (ed F. Gherardi). Invading nature; Springer series in Invasion ecology, Vol. 2.
Clergeau P, Yesou P (2006) Behavioural flexibility and numerous potential sources of introduction for the sacred ibis: causes of concern in western Europe? Biological Invasions 8: 1381-1388.
Clergeau P, Yesou P (2006) A beautiful but predating bird new to western Europe: The difficulties of management decision on the Sacred Ibises. 4th European Conf NEOBIOTA, Vienna, 27-29 September 2006.
Genovesi P (2007) - Towards a European strategy to halt biological invasions in inland waters. Pages 627-638 in: “Biological invaders in inland waters: profiles, distribution, and threats” (ed F. Gherardi). Invading nature; Springer series in Invasion ecology, Vol. 2.
Howald G, Donlan CJ, Galván J-P, Russell J, Parkes J, Samaniego A, Wang Y, Veitch D, Genovesi P, Pascal M, Saunders A, Tershy B. Invasive rodent eradication on islands. Conservation Biology, in press.
Scalera R (2007) An overview of the natural history of non indigenous amphibians and reptiles. In: Gherardi F. (editor) Biological Invaders in Inland Waters: Profiles, Distribution and Threats. Invading Nature: Springer Series in Invasion Ecology, Springer, Dordrecht, The Netherlands, Pp. 141-160.
Scalera R (2007) Virtues and shortcomings of EU legal provisions for managing NIS: Rana catesbeiana and Trachemys scripta elegans as case studies. In: Gherardi F. (editor) Biological Invaders in Inland Waters: Profiles, Distribution and Threats. Invading Nature: Springer Series in Invasion Ecology, Springer, Dordrecht, The Netherlands, Pp. 669-678.
DAISIE Methods
This website, the European Invasive Alien Species Gateway, links four individual data systems developed during the DAISIE project for public access over the internet. Click on the links below for more details on the approach taken and methods used to develop these systems:
European Alien Species Expertise Registry
Current expertise in biological invasions is distributed across research organisations throughout Europe and is funded mainly by national programmes. The European Alien Species Expertise Registry represents a fundamental step towards linking these organisations in ways that provide added value at European level and provide the critical mass of expertise in invasive alien species research to meet European-scale requirements. The European Expertise Registry is accessible to all, over the internet by searching for experts. It can be used to:
- Assemble and assess the current breadth and scope of European knowledge on alien species
- Identify experts who can contribute to the different areas of DAISIE e.g. species accounts, inventories, analysis etc.
- Facilitate the clustering and information sharing among different national programmes targeting the same invasive alien species e.g. American mink in UK, Finland etc.
- Help establish teams of experts who can, once a new alien incursion has been reported, assess the situation and prepare an action plant for the invasive alien species at a particular site. Actions plans suggest responses that are likely to be quick, effective, and can be tracked to make sure that everything possible is done to slow or arrest the spread of a potentially invasive alien species in a state or the region.
The European Expertise Registry contains details for individual experts including: contact information, taxonomic expertise, knowledge of different ecosystems, thematic areas (population ecology, management, impact assessment, current and recent research projects, publications and reports etc.). By the end of 2009, the Registry contains 1853 experts from 93 countries for 3635 taxa. Experts within the database can be searched here. The DAISIE European Alien Species Expertise Registry is likely to be the world's largest collection of information on experts and expertise on alien invasive species.
European Alien Species Database
The lack of a pan-European inventory of alien species makes it difficult to answer relatively basic questions relating to the identification, status, and trends of alien species in Europe. The DAISIE European Alien Species Database provides an up-to-date inventory of alien species known to inhabit Europe, providing a key resource for building an early detection and warning system for the Europe?s environmental managers. The Alien Species Database has been built by compiling, extending and peer-reviewing several hundred national lists of species of fungi, plants, invertebrates, fish, amphibians, reptiles, birds and mammals.
The European Alien Species Database represents a major resource and contains information on 10961 species and 69 inland and 55 coastal and marine areas, and can be searched via species names and through the geographic regions of Europe. The database aims to:
- To collate European alien marine, freshwater and terrestrial species checklists,
- To analyse cultural, taxonomic & regional differences in alien species status designation,
- To establish standardised and objective criteria for the designation alien species status,
- To apply these criteria to species checklists to identify the principal invasive species in Europe,
- To provide comparative estimates of naturalisation rates as an indication of early warning.
Geographical scope of the European Alien Species Database
The main geographic area covered by the DAISIE European Alien Species Database is the continent of Europe. For terrestrial species this includes all countries (including islands) within the continent of Europe, as well as Greenland. For coastal aquatic groups, coastlines of all European countries are included, as well as countries on the Mediterranean Sea (e.g. countries of western Asia and north Africa).
Taxonomic scope of the European Alien Species Database
The European Alien Species Database includes all species that have been introduced as a result of human activities, either intentionally or unintentionally. The database covers both invasive alien species and non-invasive alien species (see definition of terms, below).
Definition of terms
There are several terms used to name species that are transported out of their native range through human intervention, including those species that become ecological or economic problems. The DAISIE European Alien Species Database follows definitions of alien species and invasive alien species (IAS) as adopted by the Convention of Parties (COP 6, decision VI/23) supplemented by some definitions from IUCN Guidelines and ICES code of practice.
Alien species (syn: non-native, non-indigenous, foreign, exotic, introduced) - a species, subspecies or lower taxon (such as a variety, race, provenance or stock), introduced outside its natural past or present distribution; includes any part, gametes, seeds, eggs, or propagules of such species that might survive and subsequently reproduce (COP 6, decision VI/23)
Invasive alien species (IAS) (or alien invasive species) - an alien species whose introduction and/or spread threaten biological diversity (COP 6, decision VI/23)
References
IUCN 2000 - Guidelines for the prevention of Biodiversity Loss Caused by
Alien Invasive Species
IUCN 1999 - draft guidelines for the prevention of Biodiversity Loss Caused by Alien Invasive Species - not available on-line.
ICES 2003 - code of practice on the Introduction and transfer of Marine
Organisms
COP 6, decision VI/23 - on alien species that threaten ecosystems, habitats or species.
A more extensive list of cross-taxon and biome definitions of alien status and related terms can be found here.
Database fields The vocabulary defining terms used in the DAISIE European Alien Species Database are given below.
Introduction
| Intentional |
On purpose |
| Unintentional |
Unknowingly - as a by-product of human activities (parasites introduced with “intentional” aliens belong here, as they were introduced unknowingly) |
| Unknown |
Unknown |
Vector
| Dispersed |
Natural dispersal from introduced population elsewhere in Europe. If a species was introduced in one place and then it spread naturally (dispersed) into neighbouring area (e.g. Cercopagis pengoi) |
| Escaped |
Escaped from captivity/gardens/agriculture/other culture |
| Released |
Deliberate release/introduction in wild |
| Transport |
Transported accidentally |
| Hybrid |
Spontaneously generated hybrid or species descended from one, e.g. Introduced salmoniids breed with native salmonids producing less valuable hybrid forms. Hybrids created by humans do not count here |
| Unknown |
Unknown |
Pathway (used for aquatic species)
| Aquaculture |
Introduced in aquaculture, mariculture |
| Fisheries |
Stock movement, introduced as fish food; dispersal via fishing gear |
| Leisure |
Leisure activities |
| Escapes |
Animals, plants and their pests that escaped from captivity, laboratories, farms |
| Ornamental |
Live food trade, animals and plants used for ornamental purposes in parks, gardening, bonsai, etc |
| Biocontrol |
Introduced as biological control agent or pest of another species |
| Unknown |
Unknown |
Population status
| Established |
The species has formed self-reproducing populations where introduced |
| Extinct |
Once established, now extinct |
| Not established |
The species has not formed self-reproducing populations (casual, incidental) |
| Unknown |
Unknown |
Abundance
| Abundant |
Frequently occurring throughout the country in high abundances |
| Absent or extinct |
Species not available anymore |
| Common |
Although not abundant but easy to find throughout entire country |
| Local |
Patchy distribution, with higher abundance in certain localities |
| Rare |
Species observed only in certain places, low abundances |
| Single record |
Evidence based on single observation in certain locality |
| Sporadic |
Although in low abundance, species is more or less uniformly distributed throughout an area. May be related with temporary phenomena like short-time population explosions |
| Unknown |
Unknown |
European Invasive Alien Species Information System
The European Invasive Alien Species Information System focuses on 100 invasive species that threaten the natural environment of Europe. The list of species covers a range of taxonomic groups with 3 fungi, 18 terrestrial plants, 16 terrestrial invertebrates, 15 vertebrates, 16 inland water species and 32 coastal species giving a broad spectrum of life forms and functional types. These species represent some of the worst European invader species in terms of their impact on biodiversity, economy and heath, and illustrate a broad representation of impacts at different levels of ecological complexity: genetic, populations, ecosystem processes and services. A broad range of European invaded ecosystems is represented, with examples from natural and semi-natural habitats.
Species information has been authored and reviewed by DAISIE partners and/or by expert contributors from around Europe. The species accounts offer information on the biology and ecology of the species, habitat and distribution characteristics, introduction pathway, invasion trend, impacts and management methods including ways of prevention. Special emphasis was given to species impact and management. The agreed structure of the account is common, facilitating comparison among taxa. Each account for the ‘100 of the worst’ invasive species in Europe is available on this website and can be downloaded in a printable (.pdf) format. Accounts are ~650 words long and include a distribution map for Europe and photographs.
Distribution Mapping and Spatial Analysis
Biological invasions are large-scale phenomena of widespread importance and they represent one of the major threats to European biodiversity. They are characterised by remarkable spatio-temporal dynamics with many species having extended their distribution range from within a single region to much of Europe within the last century. The dramatic spread of non-native species has been facilitated by association with intercontinental commerce and travel (e.g., ballast, seed contaminants, horticultural trade), ability to disperse along regional transport networks (e.g., roadsides, canals, railways), and capacity for local colonisation and population increase. Non-native species have considerable potential to spread over large areas in a relatively short time; this places considerable urgency into integrating an understanding of spatio-temporal dynamics at the heart of invasive species management. However, up to now majority of information on the distribution of alien species in most taxonomic groups come from national mapping schemes, with no major effort to integrate at the spatial scale of the whole continent.
Distributions of the ‘100 of the worst’ invasive species have been mapped. The Common European Chronological Grid Reference System (CGRS) was used to produce distribution maps. The CGRS mapping grid is ca 50 x 50 km, depending on the latitudinal/longitudinal position, and was chosen because it employs reasonably detailed resolution for Europe and is commonly used for species mapping; this allowed the DAISIE team to collate majority of distribution data available in Europe. Data sources included national atlases, floras, faunas and databases as well as summary data available for the whole of Europe, e.g. Atlas Florae Europeae for some plant species; Mitchell-Jones et al. 1999 for mammals; updated, corrected and extended CIESM atlas for marine aliens.
The following criteria were used to map the distribution ranges of target species. For each grid, the following information was recorded: (a) known presence of the species; (b) known absence; (c) information on distribution not available. Where known, additional information on (d) species previously present but eradicated and (e) native distribution, was also considered. Where precise information on distribution was missing but the species was known to occur in a country/region/district, the distribution in these administrative units was recorded and mapped by using different colours. A different format was adopted for mapping invaders in aquatic habitats where linear distribution were represented.
Where mapping is on a regional level the World Geographical Scheme for Recording Plant Distributions has been used as a basis. As stated in this standard, "The use of any particular name to refer to a particular area in this geographical system is intended solely for the purpose of clarity of communication. It should not be taken to imply recognition of any government, any political persuasion, or any political boundary."