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Journal articles on the topic 'Biological invasions'

Author: Grafiati
Published: 4 June 2021
Last updated: 26 July 2025

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1

Rouget, Mathieu, Mark P. Robertson, John R. U. Wilson, et al. "Invasion debt - quantifying future biological invasions." Diversity and Distributions 22, no. 4 (2015): 445–56. http://dx.doi.org/10.1111/ddi.12408.

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2

Wilson, John R. U., Pablo García-Díaz, Phillip Cassey, David M. Richardson, Petr Pyšek, and Tim M. Blackburn. "Biological invasions and natural colonisations are different – the need for invasion science." NeoBiota 31 (September 14, 2016): 87–98. https://doi.org/10.3897/neobiota.31.9185.

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In a recent Discussion Paper, Hoffmann and Courchamp (2016) posed the question: are biological invasions and natural colonisations that different? This apparently simple question resonates at the core of the biological study of human-induced global change, and we strongly believe that the answer is yes: biological invasions and natural colonisations differ in processes and mechanisms in ways that are crucial for science, management, and policy. Invasion biology has, over time, developed into the broader transdisciplinary field of invasion science. At the heart of invasion science is the realis
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3

Lonsdale, W. M., and M. H. Williamson. "Biological Invasions." Journal of Applied Ecology 34, no. 1 (1997): 267. http://dx.doi.org/10.2307/2404871.

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4

Bennett, K. D., and M. Williamson. "Biological Invasions." Journal of Ecology 85, no. 3 (1997): 405. http://dx.doi.org/10.2307/2960522.

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5

Crawley, M. J., and M. Williamson. "Biological Invasions." Journal of Animal Ecology 66, no. 5 (1997): 778. http://dx.doi.org/10.2307/5934.

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6

Willis, A. J., J. A. Drake, H. A. Mooney, et al. "Biological Invasions." Journal of Ecology 79, no. 1 (1991): 261. http://dx.doi.org/10.2307/2260798.

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7

Paynter, Q. E. "Biological invasions." Biological Conservation 82, no. 2 (1997): 241. http://dx.doi.org/10.1016/s0006-3207(97)83214-4.

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8

Lee, William G. "Biological invasions." Trends in Ecology & Evolution 12, no. 6 (1997): 242–43. http://dx.doi.org/10.1016/s0169-5347(97)86964-9.

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9

Levine, Jonathan M. "Biological invasions." Current Biology 18, no. 2 (2008): R57—R60. http://dx.doi.org/10.1016/j.cub.2007.11.030.

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10

Hengeveld, R. "Mechanisms of Biological Invasions." Journal of Biogeography 15, no. 5/6 (1988): 819. https://doi.org/10.5281/zenodo.14818245.

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(Uploaded by Plazi for the Bat Literature Project) This paper considers two alternative hypotheses for explaining biological invasions. One hypothesis, currently prevalent in ecology, is based on the assumption that a 'balance of nature' exists and that biologically functional interactions dominate all other factors. An alternative hypothesis assumes that species are independent and respond individualistically to all factors, their individualism depending on speciesspecific responses relative to particular factors. The first hypothesis views community composition and external environmental fac
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11

Heger, Tina, and Ludwig Trepl. "Predicting Biological Invasions." Biological Invasions 5, no. 4 (2003): 301–9. http://dx.doi.org/10.1023/b:binv.0000005568.44154.12.

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12

Sol, Daniel. "Dissecting biological invasions." Trends in Ecology & Evolution 25, no. 3 (2010): 133. http://dx.doi.org/10.1016/j.tree.2009.10.004.

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13

Heger, Tina, Jonathan M. Jeschke, and Johannes Kollmann. "Some reflections on current invasion science and perspectives for an exciting future." NeoBiota 68 (September 17, 2021): 79–100. http://dx.doi.org/10.3897/neobiota.68.68997.

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Species spreading beyond their native ranges are important study objects in ecology and environmental sciences and research on biological invasions is thriving. Along with an increase in the number of publications, the research field is experiencing an increase in the diversity of methods applied and questions asked. This development has facilitated an upsurge in information on invasions, but it also creates conceptual and practical challenges. To provide more transparency on which kind of research is actually done in the field, the distinction between invasion science, encompassing the full s
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14

Heger, Tina, Jonathan M. Jeschke, and Johannes Kollmann. "Some reflections on current invasion science and perspectives for an exciting future." NeoBiota 68 (September 17, 2021): 79–100. https://doi.org/10.3897/neobiota.68.68997.

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Species spreading beyond their native ranges are important study objects in ecology and environmental sciences and research on biological invasions is thriving. Along with an increase in the number of publications, the research field is experiencing an increase in the diversity of methods applied and questions asked. This development has facilitated an upsurge in information on invasions, but it also creates conceptual and practical challenges. To provide more transparency on which kind of research is actually done in the field, the distinction between invasion science, encompassing the full s
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15

Liebhold, Andrew M., Timothy H. Keitt, Nikunj Goel, and Cleo Bertelsmeier. "Scale invariance in the spatial-dynamics of biological invasions." NeoBiota 62 (October 15, 2020): 269–78. http://dx.doi.org/10.3897/neobiota.62.53213.

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Despite the enormous negative consequences of biological invasions, we have a limited understanding of how spatial demography during invasions creates population patterns observed at different spatial scales. Early stages of invasions, arrival and establishment, are considered distinct from the later stage of spread, but the processes of population growth and dispersal underlie all invasion phases. Here, we argue that the spread of invading species, to a first approximation, exhibits scale invariant spatial-dynamic patterns that transcend multiple spatial scales. Dispersal from a source popula
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16

Liebhold, Andrew M., Timothy H. Keitt, Nikunj Goel, and Cleo Bertelsmeier. "Scale invariance in the spatial-dynamics of biological invasions." NeoBiota 62 (October 15, 2020): 269–78. https://doi.org/10.3897/neobiota.62.53213.

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Despite the enormous negative consequences of biological invasions, we have a limited understanding of how spatial demography during invasions creates population patterns observed at different spatial scales. Early stages of invasions, arrival and establishment, are considered distinct from the later stage of spread, but the processes of population growth and dispersal underlie all invasion phases. Here, we argue that the spread of invading species, to a first approximation, exhibits scale invariant spatial-dynamic patterns that transcend multiple spatial scales. Dispersal from a source popula
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17

Montero-Castaño, Ana, María Calviño-Cancela, Sandra Rojas-Nossa, Pilar De la Rúa, Marina Arbetman, and Carolina Laura Morales. "Biological invasions and pollinator decline." Ecosistemas 27, no. 2 (2018): 42–51. http://dx.doi.org/10.7818/ecos.1319.

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18

Adomako, Michael Opoku, Sergio Roiloa, and Fei-Hai Yu. "The COVID-19 Restrictions and Biological Invasion: A Global Terrestrial Ecosystem Perspective on Propagule Pressure and Invasion Trajectory." Sustainability 14, no. 22 (2022): 14783. http://dx.doi.org/10.3390/su142214783.

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Biological invasions driven by climate change, transportation, and intercontinental trade, as well as land-use change and tourism, pose severe threats to biodiversity and ecosystem services worldwide. However, the COVID-19-induced shutdowns and cross-border restrictions could have significantly impacted some of these drivers. Thus, COVID-19-induced restrictions may potentially alter the invasion trajectories and propagule pressure of invasive alien species, yet very few studies have examined this possibility. Here, we provide a unique conceptual framework to examine how COVID-19-induced restri
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19

Gaertner, Mirijam, Judith Fisher, Gyan Sharma, and Karen Esler. "Insights into invasion and restoration ecology: Time to collaborate towards a holistic approach to tackle biological invasions." NeoBiota 12 (February 15, 2012): 57–76. https://doi.org/10.3897/neobiota.12.2123.

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The aim of our study is to provide an integrated framework for the management of alien plant invasions, combining insights and experiences from the fields of invasion and restoration ecology to enable more effective management of invasive species. To determine linkages between the scientific outputs of the two disciplines we used an existing data base on restoration studies between 2000 and 2008 and did a bibliometric analysis. We identified the type of restoration applied, determined by the aim of the study, and conducted a content analysis on 208 selected studies with a link to biological in
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20

Cuthbert, Ross N., Angela C. Bartlett, Anna J. Turbelin, et al. "Economic costs of biological invasions in the United Kingdom." NeoBiota 67 (July 29, 2021): 299–328. http://dx.doi.org/10.3897/neobiota.67.59743.

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Although the high costs of invasion are frequently cited and are a key motivation for environmental management and policy, synthesised data on invasion costs are scarce. Here, we quantify and examine the monetary costs of biological invasions in the United Kingdom (UK) using a global synthesis of reported invasion costs. Invasive alien species have cost the UK economy between US$6.9 billion and $17.6 billion (£5.4 – £13.7 billion) in reported losses and expenses since 1976. Most costs were reported for the entire UK or Great Britain (97%); country-scale cost reporting for the UK's four constit
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21

Cuthbert, Ross N., Angela C. Bartlett, Anna J. Turbelin, et al. "Economic costs of biological invasions in the United Kingdom." NeoBiota 67 (July 29, 2021): 299–328. https://doi.org/10.3897/neobiota.67.59743.

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Although the high costs of invasion are frequently cited and are a key motivation for environmental management and policy, synthesised data on invasion costs are scarce. Here, we quantify and examine the monetary costs of biological invasions in the United Kingdom (UK) using a global synthesis of reported invasion costs. Invasive alien species have cost the UK economy between US$6.9 billion and $17.6 billion (£5.4 – £13.7 billion) in reported losses and expenses since 1976. Most costs were reported for the entire UK or Great Britain (97%); country-scale cost reporting for the UK's four constit
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22

Roura-Pascual, Núria, Brian Leung, Wolfgang Rabitsch, et al. "Alternative futures for global biological invasions." Sustainability Science 16, no. 5 (2021): 1637–50. http://dx.doi.org/10.1007/s11625-021-00963-6.

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AbstractScenario analysis has emerged as a key tool to analyze complex and uncertain future socio-ecological developments. However, currently existing global scenarios (narratives of how the world may develop) have neglected biological invasions, a major threat to biodiversity and the economy. Here, we use a novel participatory process to develop a diverse set of global biological invasion scenarios spanning a wide range of plausible global futures through to 2050. We adapted the widely used “two axes” scenario analysis approach to develop four families of four scenarios each, resulting in 16
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23

Kinlocka, Nicole L., Bracha Y. Schindler, and Jessica Gurevitch. "Biological invasions in the context of green roofs." Israel Journal of Ecology and Evolution 62, no. 1-2 (2016): 32–43. http://dx.doi.org/10.1080/15659801.2015.1028143.

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Green roofs can mitigate a number of urban environmental problems when green roof plant communities provide ecosystem services. However, this perspective may fail to address ecological aspects of the plant community. In particular, it does not account for the potential for green roofs to facilitate biological invasions. We consider current research in green roof ecology in light of the literature on biological invasions, focusing on plant invasion. We evaluate the role of species composition and novel communities, species interactions, succession, and dispersal on the trajectory of green roof
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24

Barney, Jacob N., Todd Schenk, David C. Haak, Scott Salom, Bryan Brown, and Erin R. Hotchkiss. "Building Partnerships and Bridging Science and Policy to Address the Biological Invasions Crisis." Invasive Plant Science and Management 12, no. 1 (2019): 74–78. http://dx.doi.org/10.1017/inp.2018.33.

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AbstractBiological invasions are one of the grand challenges facing society, as exotic species introductions continue to rise and can result in dramatic changes to native ecosystems and economies. The scale of the “biological invasions crisis” spans from hyperlocal to international, involving a myriad of actors focused on mitigating and preventing biological invasions. However, the level of engagement among stakeholders and opportunities to collaboratively solve invasives issues in transdisciplinary ways is poorly understood. The Biological Invasions: Confronting a Crisis workshop engaged a br
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25

Bonnaud, Elsa. "Biological Invasions 2020 Horizon." Diversity 12, no. 2 (2020): 77. http://dx.doi.org/10.3390/d12020077.

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This special issue points to the necessity to continue actively working on biological invasions, as invasive species remain a main and global threat for biodiversity through a global homogenization process. This issue includes six research papers, covering a large range of taxa, studying new invasive processes and proposing innovative management solutions. The way forward will be to continue working in close relation with other stakeholders and decision-makers, increase communication efforts, solicit societal feedback, and quickly implement consistent legislation.
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26

Taylor, R. A. J., and Rob Hengeveld. "Dynamics of Biological Invasions." Journal of Animal Ecology 59, no. 3 (1990): 1198. http://dx.doi.org/10.2307/5046.

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27

North, P. M., and R. Hengeveld. "Dynamics of Biological Invasions." Biometrics 47, no. 1 (1991): 351. http://dx.doi.org/10.2307/2532532.

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28

Hengeveld, R. "Mechanisms of Biological Invasions." Journal of Biogeography 15, no. 5/6 (1988): 819. http://dx.doi.org/10.2307/2845342.

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29

Dehnen-schmutz, Katharina, and Mark Williamson. "BIOLOGICAL INVASIONS IN EUROPE." Diversity and Distributions 9, no. 6 (2003): 485–86. http://dx.doi.org/10.1046/j.1472-4642.2003.00041.x.

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30

Duffey, Eric. "Dynamics of biological invasions." Biological Conservation 52, no. 4 (1990): 323. http://dx.doi.org/10.1016/0006-3207(90)90080-9.

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31

Ricciardi, Anthony. "Biological Invasions Simply Explained." BioScience 64, no. 2 (2014): 154–55. http://dx.doi.org/10.1093/biosci/bit023.

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32

Jarić, Ivan, Tina Heger, Federico Castro Monzon, et al. "Crypticity in Biological Invasions." Trends in Ecology & Evolution 34, no. 4 (2019): 291–302. http://dx.doi.org/10.1016/j.tree.2018.12.008.

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33

Daehler, Curtis C., and Donald R. Strong. "Prediction and biological invasions." Trends in Ecology & Evolution 8, no. 10 (1993): 380. http://dx.doi.org/10.1016/0169-5347(93)90227-g.

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34

Duprey, Joe, Ramón Gallego, Terrie Klinger, and Ryan P. Kelly. "Environmental DNA reveals patterns of biological invasion in an inland sea." PLOS ONE 18, no. 12 (2023): e0281525. http://dx.doi.org/10.1371/journal.pone.0281525.

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Non-native species have the potential to cause ecological and economic harm to coastal and estuarine ecosystems. Understanding which habitat types are most vulnerable to biological invasions, where invasions originate, and the vectors by which they arrive can help direct limited resources to prevent or mitigate ecological and socio-economic harm. Information about the occurrence of non-native species can help guide interventions at all stages of invasion, from first introduction, to naturalization and invasion. However, monitoring at relevant scales requires considerable investment of time, re
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35

Watari, Yuya, Hirotaka Komine, Elena Angulo, Christophe Diagne, Liliana Ballesteros-Mejia, and Franck Courchamp. "First synthesis of the economic costs of biological invasions in Japan." NeoBiota 67 (July 29, 2021): 79–101. http://dx.doi.org/10.3897/neobiota.67.59186.

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Despite the large body of knowledge recognising the impact of biological invasions on biodiversity, their economic impact has been less evaluated. However, the associated economic costs ought to provide useful information on many different aspects to prevent and manage invasions. Here, we describe the economic costs of biological invasions in Japan using InvaCost, a recently-published global database on monetary costs extracted from English and non-English sources, as well as a complementary search, thereby filling a gap in regional knowledge. We focused on the following four dimensions when a
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36

Watari, Yuya, Hirotaka Komine, Elena Angulo, Christophe Diagne, Liliana Ballesteros-Mejia, and Franck Courchamp. "First synthesis of the economic costs of biological invasions in Japan." NeoBiota 67 (July 29, 2021): 79–101. https://doi.org/10.3897/neobiota.67.59186.

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Despite the large body of knowledge recognising the impact of biological invasions on biodiversity, their economic impact has been less evaluated. However, the associated economic costs ought to provide useful information on many different aspects to prevent and manage invasions. Here, we describe the economic costs of biological invasions in Japan using InvaCost, a recently-published global database on monetary costs extracted from English and non-English sources, as well as a complementary search, thereby filling a gap in regional knowledge. We focused on the following four dimensions when a
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37

Kirichenko, Natalia, Phillip J. Haubrock, Ross N. Cuthbert, et al. "Economic costs of biological invasions in terrestrial ecosystems in Russia." NeoBiota 67 (July 29, 2021): 103–30. http://dx.doi.org/10.3897/neobiota.67.58529.

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Terrestrial ecosystems, owing to the presence of key socio-economic sectors such as agriculture and forestry, may be particularly economically affected by biological invasions. The present study uses a subset of the recently developed database of global economic costs of biological invasions (InvaCost) to quantify the monetary costs of biological invasions in Russia, the largest country in the world that spans two continents. From 2007 up to 2019, invasions costed the Russian economy at least US$ 51.52 billion (RUB 1.38 trillion, n = 94 cost entries), with the vast majority of these costs base
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38

Kirichenko, Natalia, Phillip J. Haubrock, Ross N. Cuthbert, et al. "Economic costs of biological invasions in terrestrial ecosystems in Russia." NeoBiota 67 (July 29, 2021): 103–30. https://doi.org/10.3897/neobiota.67.58529.

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Terrestrial ecosystems, owing to the presence of key socio-economic sectors such as agriculture and forestry, may be particularly economically affected by biological invasions. The present study uses a subset of the recently developed database of global economic costs of biological invasions (InvaCost) to quantify the monetary costs of biological invasions in Russia, the largest country in the world that spans two continents. From 2007 up to 2019, invasions costed the Russian economy at least US$ 51.52 billion (RUB 1.38 trillion, n = 94 cost entries), with the vast majority of these costs base
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39

Saul, Wolf-Christian, Jonathan Jeschke, and Tina Heger. "The role of eco-evolutionary experience in invasion success." NeoBiota 17 (June 28, 2013): 57–74. https://doi.org/10.3897/neobiota.17.5208.

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Invasion ecology has made considerable progress in identifying specific mechanisms that potentially determine success and failure of biological invasions. Increasingly, efforts are being made to interrelate or even synthesize the growing number of hypotheses in order to gain a more comprehensive and integrative understanding of invasions. We argue that adopting an eco-evolutionary perspective on invasions is a promising approach to achieve such integration. It emphasizes the evolutionary antecedents of invasions, i.e. the species’ evolutionary legacy and its role in shaping novel biotic intera
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40

Sinclair, James S., Jeffrey A. Brown, and Julie L. Lockwood. "Reciprocal human-natural system feedback loops within the invasion process." NeoBiota 62 (October 15, 2020): 489–508. http://dx.doi.org/10.3897/neobiota.62.52664.

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Biological invasions are inextricably linked to how people collect, move, interact with and perceive non-native species. However, invasion frameworks generally do not consider reciprocal interactions between non-native species and people. Non-native species can shape human actions via beneficial or detrimental ecological and socioeconomic effects and people, in turn, shape invasions through their movements, behaviour and how they respond to the collection, transport, introduction and spread of non-natives. The feedbacks that stem from this ‘coupled human and natural system’ (CHANS) could there
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41

Sinclair, James S., Jeffrey A. Brown, and Julie L. Lockwood. "Reciprocal human-natural system feedback loops within the invasion process." NeoBiota 62 (October 15, 2020): 489–508. https://doi.org/10.3897/neobiota.62.52664.

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Biological invasions are inextricably linked to how people collect, move, interact with and perceive non-native species. However, invasion frameworks generally do not consider reciprocal interactions between non-native species and people. Non-native species can shape human actions via beneficial or detrimental ecological and socioeconomic effects and people, in turn, shape invasions through their movements, behaviour and how they respond to the collection, transport, introduction and spread of non-natives. The feedbacks that stem from this 'coupled human and natural system' (CHANS) could there
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42

Dgebuadze, Yu Yu. "BIOLOGICAL INVASIONS OF ALIEN SPECIES – A GLOBAL CHALLENGE IN THE LAST DECADES." Вестник Российской академии наук 93, no. 9 (2023): 814–23. http://dx.doi.org/10.31857/s0869587323090050.

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Biological invasions of alien species – the occupation by living organisms of territories and water areas outside their historical range – have now acquired a gigantic scale, affecting all countries and continents. The recent trends in the development of the invasive process indicate its significant intensification. The proposed review provides information on the scale of biological invasions on Earth, history, current state and main directions of scientific research in this area. In particular, the factors that determine the possibility of invasion of an alien species are considered; stages o
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43

Sullivan, Lauren L., Bingtuan Li, Tom E. X. Miller, Michael G. Neubert, and Allison K. Shaw. "Density dependence in demography and dispersal generates fluctuating invasion speeds." Proceedings of the National Academy of Sciences 114, no. 19 (2017): 5053–58. http://dx.doi.org/10.1073/pnas.1618744114.

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Density dependence plays an important role in population regulation and is known to generate temporal fluctuations in population density. However, the ways in which density dependence affects spatial population processes, such as species invasions, are less understood. Although classical ecological theory suggests that invasions should advance at a constant speed, empirical work is illuminating the highly variable nature of biological invasions, which often exhibit nonconstant spreading speeds, even in simple, controlled settings. Here, we explore endogenous density dependence as a mechanism f
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44

Hulme, Philip E., Richard Baker, Robert Freckleton, et al. "The Epidemiological Framework for Biological Invasions (EFBI): an interdisciplinary foundation for the assessment of biosecurity threats." NeoBiota 62 (October 15, 2020): 161–92. http://dx.doi.org/10.3897/neobiota.62.52463.

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Emerging microparasite (e.g. viruses, bacteria, protozoa and fungi) epidemics and the introduction of non-native pests and weeds are major biosecurity threats worldwide. The likelihood of these threats is often estimated from probabilities of their entry, establishment, spread and ease of prevention. If ecosystems are considered equivalent to hosts, then compartment disease models should provide a useful framework for understanding the processes that underpin non-native species invasions. To enable greater cross-fertilisation between these two disciplines, the Epidemiological Framework for Bio
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45

Hulme, Philip E., Richard Baker, Robert Freckleton, et al. "The Epidemiological Framework for Biological Invasions (EFBI): an interdisciplinary foundation for the assessment of biosecurity threats." NeoBiota 62 (October 15, 2020): 161–92. https://doi.org/10.3897/neobiota.62.52463.

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Emerging microparasite (e.g. viruses, bacteria, protozoa and fungi) epidemics and the introduction of non-native pests and weeds are major biosecurity threats worldwide. The likelihood of these threats is often estimated from probabilities of their entry, establishment, spread and ease of prevention. If ecosystems are considered equivalent to hosts, then compartment disease models should provide a useful framework for understanding the processes that underpin non-native species invasions. To enable greater cross-fertilisation between these two disciplines, the Epidemiological Framework for Bio
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46

Dytham, Calvin, N. Shigesada, and K. Kawasaki. "Biological Invasions: Theory and Practice." Journal of Animal Ecology 66, no. 6 (1997): 918. http://dx.doi.org/10.2307/6013.

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47

Papacostas, KJ, EW Rielly-Carroll, SE Georgian, et al. "Biological mechanisms of marine invasions." Marine Ecology Progress Series 565 (February 17, 2017): 251–68. http://dx.doi.org/10.3354/meps12001.

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48

Carlton, James T. "Biological Invasions and Cryptogenic Species." Ecology 77, no. 6 (1996): 1653–55. http://dx.doi.org/10.2307/2265767.

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49

Meyerson, Laura A., and Daniel Simberloff. "The journal Biological Invasions evolves." Biological Invasions 24, no. 2 (2021): 319–20. http://dx.doi.org/10.1007/s10530-021-02663-9.

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50

Ravi, Sujith, Paolo D’Odorico, Scott L. Collins, and Travis E. Huxman. "Can biological invasions induce desertification?" New Phytologist 181, no. 3 (2009): 512–15. http://dx.doi.org/10.1111/j.1469-8137.2009.02736.x.

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