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Effects of Invasive Non-Native Species on the Native Biodiversity in the River Rhine 273 Van der Velde G, Rajagopal S, Van den Brink FWB, Kelleher B, Paffen BGP, Kempers AJ, Bij de Vaate A (1998) Ecological impact of an exotic amphipod invasion in the river Rhine. In: Nienhuis PH, Leuven RSEW, Ragas AMJ (eds) New concepts for sustainable management of river basins. Backhuys, Leiden, pp 159–169 Van der Velde G, Nagelkerken I, Rajagopal S, Bij de Vaate A (2002) Invasions by alien species in inland freshwater bodies in Western Europe: the Rhine delta. In: Leppäkoski E, Gollasch S, Olenin S (eds) Invasive aquatic species of Europe. Distribution, impacts and management. Kluwer, Dordrecht, pp 360–372 Van Geest GJ, Coops H, Roijackers RMM, Buijse AD, Scheffer M (2005) Succession of aquatic vegetation driven by reduced water-level fluctuation in floodplain lakes. J Appl Ecol 42:251–260 Van Urk G (1984) Lower Rhine-Meuse. In: Whitton BA (ed) Ecology of European rivers. Blackwell, Oxford, pp 437–468 Williamson M (1996) Biological invasions. Chapman and Hall, London Williamson M (1999) Invasions. Ecography 22:5–12
16 Hybridization and Introgression Between Native and Alien Species Carlo R. Largiadèr 16.1 Introduction Human activities, such intentional and unintentional transplantations, and habitat alterations including the establishment of migration corridors, generate increasing opportunities for formerly allopatric taxa to meet and to hybridize. There is indeed increasing evidence that these introduced plant and animal taxa (including crop plants and domesticated animal taxa) frequently hybridize with native relatives and with other introduced taxa, leading to a growing concern that these hybridizations may compromise the genetic integrity of native taxa to the point of causing extinctions (Abbott 1992; Rhymer and Simberloff 1996; Levin et al. 1996; Ellstrand and Schierenbeck 2000; Vilà et al. 2000). A decade ago, Rhymer and Simberloff (1996) stated in their review on this topic that the known cases are probably just the tip of the iceberg. Using the search term ‘hybridization and introgression’, the Web of Science database yields a total of 1,178 research articles, of which 935 (or 80 %) have been published after 1995 (Fig. 16.1). Indeed, the evidence for natural and man-induced hybridization and introgression appears to have increased exponentially these last few years. Presently, we still cannot answer the questions of how widespread and how important these processes are in the context of biological invasions. However, regarding the dramatic increase of evidence in the literature, we can already conclude that natural and anthropogenic hybridization and introgression are very frequent, and play an important role in animal and plant species, both at the inter- and intraspecific level. It is also very likely that this evidence will continue to grow – probably many cases of hybridization and introgression have so far remained unnoticed, because hybrids may be rare and because, in morphologically uniform groups, they are difficult to recognize. Furthermore, many taxa are still unknown, and many taxonomic groups and geographic areas are understudied. Finally, the manner in which hybridization Ecological Studies,Vol. 193 W. Nentwig (Ed.) Biological Invasions © Springer-Verlag Berlin Heidelberg 2007
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Ecological Studies,Vol. 193 Analysi
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W. Nentwig (Ed.) Biological Invasio
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Preface Yet another book on “Biol
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Contents 1 Biological Invasions: wh
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Contents 5 Waterways as Invasion Hi
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Contents Section III Patterns of In
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Contents Section IV Ecological Impa
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Contents 16.5.1 Genetic Differentia
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Contents XVII 19.4.5 Scenario Devel
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Contents XIX 23 Pros and Cons of Bi
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XXII Contributors Buschmann, Holger
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XXIV Contributors Nentwig, Wolfgang
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1 Biological Invasions: why it Matt
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Biological Invasions: why it Matter
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Biological Invasions: why it Matter
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Section I Pathways of Biological In
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2 Pathways in Animal Invasions Wolf
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Pathways in Animal Invasions 13 Ser
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Pathways in Animal Invasions 15 and
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Pathways in Animal Invasions 17 hou
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Pathways in Animal Invasions 19 (Eq
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Pathways in Animal Invasions 21 wat
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Pathways in Animal Invasions 23 2.3
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Pathways in Animal Invasions 25 adv
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Pathways in Animal Invasions 27 Lon
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30 I. Kowarik and M. von der Lippe
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40 3.4.2.1 Adhesion to Vehicles I.
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42 3.4.3 Role of Living Conveyers I
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4 Is Ballast Water a Major Dispersa
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Is Bllast Water a Major Dispersal M
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60 B.S. Galil, S. Nehring, and V. P
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Short Introduction Wolfgang Nentwig
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80 R.A. Hufbauer and M.E. Torchin s
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82 6.2 Hypotheses to Explain Biolog
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84 R.A. Hufbauer and M.E. Torchin e
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86 R.A. Hufbauer and M.E. Torchin l
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88 R.A. Hufbauer and M.E. Torchin (
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90 R.A. Hufbauer and M.E. Torchin i
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92 R.A. Hufbauer and M.E. Torchin h
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94 R.A. Hufbauer and M.E. Torchin B
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96 R.A. Hufbauer and M.E. Torchin T
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98 P. Pysšek and D.M. Richardson a
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100 P. Pysšek and D.M. Richardson
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114 7.3.1 Assumptions for Congeneri
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122 References P. Pysšek and D.M.
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8 Do Successful Invaders Exist? Pre
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Do Successful Invaders Exist? 129 F
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Do Successful Invaders Exist? 131 l
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Do Successful Invaders Exist? 133 T
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Do Successful Invaders Exist? 135 a
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Do Successful Invaders Exist? 137 b
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Do Successful Invaders Exist? 139 m
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Do Successful Invaders Exist? 141 R
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148 M.L. Brooks ment practices desi
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150 M.L. Brooks direct additions to
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152 M.L. Brooks lerberg 1998, 2002;
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154 M.L. Brooks native plants, as d
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156 M.L. Brooks methods used to rem
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158 9.4.2 Effects of Vegetation Man
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160 M.L. Brooks potential associate
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162 M.L. Brooks Schmidt W (1989) Pl
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164 M. Scherer-Lorenzen, H. Olde Ve
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182 I. Kühn and S. Klotz who provi
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184 11.3 Case Studies on Ecosystem
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186 I. Kühn and S. Klotz fore, und
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188 I. Kühn and S. Klotz home soil
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190 I. Kühn and S. Klotz evolution
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192 I. Kühn and S. Klotz Similarly
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194 I. Kühn and S. Klotz To increa
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196 I. Kühn and S. Klotz Mack MC,
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198 W. Thuiller, D.M. Richardson, a
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Section IV Ecological Impact of Bio
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216 Section IV · Short Introductio
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218 H. Charles and J.S. Dukes proce
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Plant,Animal, and Microbe Invasive
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Plant,Animal, and Microbe Invasive
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19 Socio-Economic Impact and Assess
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Socio-Economic Impact and Assessmen
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354 J. Touza, K. Dehnen-Schmutz, an
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368 G. J. Hallman thought to be due
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370 G. J. Hallman (WTO), and, there
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372 G. J. Hallman literature to des
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374 21.3.2 Phytosanitary Treatments
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376 G. J. Hallman foliage, even tho
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378 G. J. Hallman initiated, and th
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380 G. J. Hallman Fig. 21.1 Boxes o
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382 G. J. Hallman tosanitary treatm
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384 G. J. Hallman Jones WW, Holzman
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386 P. Genovesi invasive alien spec
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388 100000 Area of islands successf
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390 P. Genovesi ing all the removal
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392 P. Genovesi efficacy of removal
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394 P. Genovesi 11 years (Panzacchi
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396 22.2.6 Human Dimensions P. Geno
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398 P. Genovesi delayed by lengthy
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400 P. Genovesi Acknowledgements. F
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402 P. Genovesi Panzacchi M, Bertol
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404 23.2 Pros of Biological Control
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406 D. Babendreier pods, agents rel
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408 D. Babendreier strated that par
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410 D. Babendreier In addition to t
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412 D. Babendreier As another facto
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414 D. Babendreier has attracted co
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416 D. Babendreier conducting caref
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418 D. Babendreier Michaud JP (2002
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420 W. Nentwig widely accepted that
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422 to minimize the spread of alien
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Subject Index A Abies grandis 334 a
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Subject Index 427 bird 5, 22, 130-1
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Subject Index 429 cost-benefit 339,
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Subject Index 431 fallow deer 19 fa
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Subject Index 433 inbreeding depres
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Subject Index 435 Murdannia 118 Mus
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Subject Index 437 potato 361 poultr
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Subject Index 439 Sirex noctillo 33
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Subject Index 441 - table 92, 225,
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