Pan‐continental invasion of Pseudorasbora parva: towards a better understanding of freshwater fish invasions

Fish and Fisheries - Tập 11 Số 4 - Trang 315-340 - 2010
Rodolphe E. Gozlan1, Demetra Andreou2, Takashi Asaeda3, Kathleen Beyer4, Rachid Bouhadad5, Dean Burnard2, Nuño Caiola6, P. Cakić7, Vesna Djikanović7, Hamid Reza Esmaeili8, I. Falka9, Duncan Golicher1, Ákos Harka10, Galina Jeney11, Vladimír Kováč12, Jiří Musil13, Annamaria Nocita14, Meta Povž15, Nicolas Poulet16, Tomas Virbickas17, Christian Wolter18, Ali Serhan Tarkan19, Elena Tricarico20, Teodora Trichkova21, Hugo Verreycken22, Andrzej Witkowski23, Chun Guang Zhang24, Irene Zweimueller25, J. Robert Britton1
1School of Conservation Sciences, Bournemouth University, Talbot Campus, Fern Barrow, Poole, Dorset, BH12 5BB, UK
2Cardiff School of Biosciences, Biomedical Building, Museum Avenue, Cardiff, CF10 3US, UK
3Department of Environmental Science, Saitama University, 255 Shimo‐okubo, Sakura, Saitama 338‐8570, Japan
4SARDI Aquatic Sciences, PO Box 120, Henley Beach, Adelaide, SA 5022, Australia
5USTHB University, BP 32, El Alia, Bab Ezzouar, Algeria
6IRTA Aquatic Ecosystems, Ctra. de Poble Nou, Km 5.5, Sant Carles de la Ràpita E‐43540, Spain
7Institute for Biological Research ‘Sinisa Stankovic’, 142 Despota Stefana Blvd, University of Belgrade, 11060 Belgrade, Serbia
8Department of Biology, College of Sciences, Shiraz University, Shiraz 71454, Iran
9Mureş Water Directorate, Târgu‐Mureş, Romania
10Hungarian Ichthyological Society, Tancsics 1, 5350 Tiszafured Hungary
11Research Institute for Fisheries, Aquaculture and Irrigation, Anna liget 8, 5540 Szarvas, Hungary
12Department of Ecology, Faculty of Natural Sciences, Comenius University, Mlynská dolina B2, Bratislava, Slovakia
13Department of Aquatic Ecology, T.G.M. Water Research Institute, Podbabská 30, 160 00 Praha 6, Czech Republic
14Museum of Natural History, Zoology Section, University of Florence, Via Romana 17, Florence, Italy
15Umbra, Institute of Natural Sciences, Ulica bratov Ucakar 108, 1000 Ljubljana, Slovenia
16ONEMA, Office de l’Eau et des Milieux Aquatiques (the French National Agency for Water and Aquatic Ecosystems), 16 Avenue Louison‐Bobet, 94132 Fontenay‐sous‐Bois, France
17Department of Aquatic Ecosystems, Institute of Ecology, Akademijos 2, LT‐08412 Vilnius, Lithuania
18Leibniz Institute of Freshwater Ecology and Inland Fisheries, Müggelseedamm 310, 12587 Berlin, Germany
19Faculty of Fisheries, Muğla University, 4800, Kötekli, Muğla, Turkey
20Dip. Biologia Evoluzionistica “Leo Pardi” Universita' degli Studi di Firenze, via Romana 17 I‐50125, Firenze, Italy
21Institute of Zoology, Bulgarian Academy of Sciences, 1 Tsar Osvoboditel Blvd., Sofia 1000, Bulgaria
22Research Institute for Nature and Forest (INBO), Duboislaan 14, B-1560 Hoeilaart, Belgium
23Museum of Natural History, Wrocław University, Sienkiewicza 21, 50-335 Wrocław, Poland
24Institute of Zoology, Chinese Academy of Sciences, Chaoyang District, Beijing, 100101, China
25Department of Freshwater Ecology, Faculty of Life Sciences, University of Vienna, Althanstr. 14, A-1090 Vienna, Austria

Tóm tắt

Abstract

In recent years, policy‐makers have sought the development of appropriate tools to prevent and manage introductions of invasive species. However, these tools are not well suited for introductions of non‐target species that are unknowingly released alongside intentionally‐introduced species. The most compelling example of such invasion is arguably the topmouth gudgeon Pseudorasbora parva, a small cyprinid species originating from East Asia. A combination of sociological, economical and biological factors has fuelled their rapid invasion since the 1960s; 32 countries (from Central Asia to North Africa) have been invaded in less than 50 years. Based on a combination of monitoring surveys (2535 populations sampled) and literature reviews, this paper aims to quantify and characterise important invasion parameters, such as pathways of introduction, time between introduction and detection, lag phase and plasticity of life history traits. Every decade, five new countries have reported P. parva introduction, mainly resulting from the movement of Chinese carps for fish farming. The mean detection period after first introduction was 4 years, a duration insufficient to prevent their pan‐continental invasion. High phenotypic plasticity in fitness related traits such as growth, early maturity, fecundity, reproductive behaviour and the ability to cope with novel pathogens has predisposed P. parva to being a strong invader. The Pseudorasbora parva invasion has provided quantitative data for the development of 1) early warning systems across different spatial scales; 2) rapid eradication programmes prior to natural spread in open systems and 3) sound risk assessments with emphasis on plasticity of life history traits.

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Fish and Fisheries

Tập 11 Số 4

315-340

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