A proposed unified framework for biological invasions.

By T. Blackburn, Petr Pyšek, S. Bacher, James T. Carlton, R. Duncan, V. Jarošı́k, John R. U. Wilson, D. Richardson. Trends in Ecology & Evolution, 2011

2,453 citations recorded by the source corpus.

Subfields: Ecology, Insect Science, Nature and Landscape Conservation

View Paper: https://www.semanticscholar.org/paper/755ec5de3e7d5c22fb401d1e2110fb6f8e0cd2df

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Citations in the corpus

The role of species charisma in biological invasions (2020, background): “Charisma probably has negligible effects on inadvertent introductions (eg via ballast water or seed contamination) or those mainly driven by perceived utility (eg crop species), but we postulate that charismatic species should have a comparatively higher overall chance Blackburn et al .”
Projecting the continental accumulation of alien species through to 2050 (2020, neutral): “The analysis was based on the Alien Species First Records data-base (Seebens et al., 2017, 2018), which contains first records of alien species that have become established—that is, forming permanent self-sustaining populations (Blackburn et al., 2011)—in one or more mainland or island regions.”
Alien species as a driver of recent extinctions (2016, background): “Human activities have also greatly increased the rates of immigration [5,6], by deliberately or accidentally transporting and introducing large numbers of species to areas beyond normal biogeographic barriers to their spread, where they may establish viable populations (here termed alien) [7].”
Identifying the role of soil microbes in plant invasions (2016, background): “However, only a fraction of introduced plant species become invasive (i.e. widespread in the introduced range, sensu Blackburn et al. (2011)), and abundant at a local scale in invaded plant communities.”
Changes in the composition and distribution of alien plants in South Africa: An update from the Southern African Plant Invaders Atlas (2017, methodology): “Similarly, while SAPIA provides some indication of the introduction status of species, a separate process is required to list all alien plants in the country and to confirm their status along the introduction–naturalisation–invasion continuum as per Blackburn et al. (2011). There have been several a”
Temporal and interspecific variation in rates of spread for insect species invading Europe during the last 200 years (2016, background): “Biological invasions by alien species involve a series of discrete, consecutive phases (Blackburn et al. 2011; Lockwood et al. 2013).”
Ecology of forest insect invasions (2017, background): “These species have succeeded in overcoming multiple barriers along the successive universal phases of invasions that are transport and arrival, establishment in an invaded area, spread and impact (Liebhold and Tobin 2008; Blackburn et al. 2011).”
Diversity, biogeography and the global flows of alien amphibians and reptiles (2017, methodology): “We focused on established alien species, defined as those that do not occur naturally in a region and form self- sustaining, introduced populations in that region (Blackburn et al., 2011).”
The role of eco-evolutionary experience in invasion success (2013, neutral): “Accordingly, increasing efforts are being made to interconnect or even synthesize the growing number of hypotheses and concepts (e.g. Catford et al. 2009, Blackburn et al. 2011, Gurevitch et al. 2011).”
The Worldwide Spread, Success, and Impact of Ragweed (Ambrosia spp.) (2017, background): “Biological invasions can be represented as a chronological series of decisive stages that can allow or halt the entry and establishment of an organism in a new range (Blackburn et al., 2011; Richardson and Pysek, 2012).”
Soil seed banks in plant invasions: promoting species invasiveness and long-term impact on plant community dynamics. (2012, background): “However, separating the two groups of aliens according to the stage of invasion (sensu Richardson et al. 2000b, Blackburn et al. 2011) reveals a striking pattern, with the proportion of species reported to form long-term persistent seed banks increasing from casual to naturalized to invasive (Fig.”
Fistularia commersonii in the Mediterranean Sea: invasion history and distribution modeling based on presence-only records (2013, background): “Finally, at the intra-annual level, the distribution of our records was clearly skewed towards the coldseason , especially towards the period October– December, as already noted by Occhipinti-Ambrogi and Galil (2008) and by Bodilis et al. (2011).”