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1 September 2013 How to Become a Successful Invader
Nan-Yao Su
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Most invasive species hitchhike on human transportation, and their close associations with human activity increase their chances of uptake. Once aboard, potential invaders have to survive the journey, and those with traits such as being a general feeder or tolerance to a wide range of environmental conditions tend to survive the transportation better. Similar traits are generally considered to also aid their establishment in new habitats, but studies showed that the propagule pressure, not any of the species-specific traits, is the most important factor contributing to their successful establishment. Higher propagule pressure, i.e., repeated invasions of larger numbers of individuals, reduces Allee effects and aids the population growth of invasive species in alien lands. Coined as the invasive bridgehead effect, repeated introduction also selects a more invasive population that serves as the source of further invasions to other areas. Invasive species is the consequence of homogenocene (our current ecological epoch with diminished biodiversity and increasing similarity among ecosystems worldwide) that began with the Columbian Exchange of the 15th century and possibly the Pax Mongolica of the 13–14th century. Anthropogenic movement of goods among major cities will only accelerate, and the heightened propagule pressure will increase the number of invasive species for as long as the current practices of global commercial activities continue.

Of the over 12,500 insect species found in Florida in 1995, 988 (7.9%) were listed as “non-native” species (Frank & McCoy 1995), but not all of them are considered “invasive.” Invasive species are defined as the non-native “pest” species, i.e., those that adversely affect environment, economy and human health (Anonymous 1999). Pest status is determined primarily by human value and perception. Following its successful introduction to control cacti (Opuntia spp.) (Caryophyllales: Cactaceae) in Australia in 1925, for example, the moth Cactoblastis cactorum Berg (Lepidoptera: Pyralidae) was intentionally introduced to several Caribbean islands in 1957 (Frank & McCoy 1995) to control Opuntia weeds. By 1989, C. cactorum had spread to the Florida Keys where it became a “pest” because it began to attack two cati, O. spinosissima Martyn (Mill.) and O. triacantha (Willdenow), which are considered to have value because they are designated rare (Habeck & Bennett 1990).

Certain species-specific characteristics are often regarded as traits that render some species more “invasive.” These include, among others, high dispersal ability (better survival of transportation), association with human activity (increasing opportunities for migration), ecological competence (better survival in a new environment), rapid and/or placid reproduction (e.g., sexual and asexual reproduction), and rapid population growth. The usefulness of the list of such “invasive” traits has been questioned because many species with these traits have never become invasive (Kolar & Lodge 2001). These traits may be “necessary“ instead of “sufficient,” but they still serve as the guide to understand the likelihood of a species to become invasive.


Uptake and Migration

Most cases of species invasions are humanmediated. Living organisms extend their ranges naturally, but natural extension of most species occurs less frequently and at much shorter distances than anthropogenic events. Because most invasive species hitchhike on human transportation, a close association with human activity increases their chances of uptake. Cockroaches, rodents and some termite species tend to live near human habitat and are frequently transported. The Formosan subterranean termite, Coptotermes formosanus Shiraki (Isoptera: Rhinotermitidae), for example, tends to infest man-made structures (hence the common name in its native China is “house termite”), and is one of the most widely distributed subterranean termites (Rust & Su 2012). The West Indies powderpost termite, Cryptotermes brevis Walker (Isoptera: Kalotermitidae), often hitchhikes in wooden furniture or picture frames (and thus nicknamed “furniture termite”), and is found in more regions in the world than any other termite species.

Once aboard, the stowaway has to survive the journey (Fig. 1). General feeders that can tolerate a wider range of temperature and humidity tend to survive better during the transportation, but some species may create conditions suitable for their survival. Incipient colonies of C. formosanus, for example, may seal off the nest after tunneling into wet wood, and create moist conditions in their food source to survive the journey.

Fig. 1.

Steps for a species to become a successful invader in alien lands.


Surviving in a New Environment: Propagule Pressure

Species-specific traits that better serve for survival during transportation (i.e., generalist feeders, and tolerance to a wide range of environmental conditions) are usually considered to aid the invaders to survive in new environment. Colautti et al. (2006) who studied 14 invasive characteristics (i.e., features associated with invasive species), however, found that propagule pressure was the only consistent predictor of invasiveness. Physiological tolerance and body size did not have any effect on a species' ability to invade a foreign land. Propagule pressure is defined as the measure of the total number of individuals being introduced, and is the function of the number of introduction events and the mean number of introduced individuals per event (Lockwood et al. 2005) (Fig. 1). Generally speaking, more introduction events with more individuals per event increase the propagule pressure and hence the chance of successful establishment (Colautti et al. 2006). Propagule pressure is affected by invasion pathways that are closely associated with human activities. Using the mitochondrial DNA sequences, Yang et al. (2012) examined the invasion pathways of the fire ant, Solenopsis invicta Buren (Hymenoptera: Formicidae), into China and showed that this species was most likely imported from Austin, Texas, which also ranked the highest in exporting goods to China. The frequent traffic of goods from Austin to China apparently increased the propagule pressure and aided its successful invasion.

Population Growth and Allee Effect

The notion that density dependent factors govern the upper limit of population size goes back as far as Malthus and forms the backdrop for natural selection. However, low population density during the early stage of species establishment may also inhibit population growth due to infrequent intra-species encounters. Coined the “Allee effect,” this principle was demonstrated in a series of studies using goldfish (Allee 1931; Allee & Bowen 1932) during the time when most ecologists were focusing on the adverse effects of overcrowding and competition on individual survival. Overcrowding increased individual competition and mortality thus inhibits population growth, but according to the Allee effect, undercrowding also deters population growth due to these aggregation-related consequences. Mechanisms contributing to the Allee effect may include mate limitation, cooperative defense, cooperative feeding, and environmental alternation through aggregation. Leung et al. (2004), for example, used prediction models to study zebra mussel invasions in 1,589 inland lakes of Michigan and found that models that included the Allee effect were better in predicting its invasion. Due to the Allee effect, higher propagule pressure increases the probability for invasive species to establish in a new environment, and to increase its population (Fig. 1).

Range Expansion and Invasive Bridgehead Effect

Many species do not establish in alien lands despite being frequently transported by man, be it intentionally or accidentally (Lockwood et al. 2005). The frequent anthropogenic movement of these species may act as a process to select a particular population that is more invasive than others. Once established, the selected population, instead of the populations in the native land, may become the source of further invasions to other regions and range expansion (Fig. 1). This phenomenon was termed “invasive bridgehead effect” by Lombaert et al. (2010) who tracked the invasive pathways of the Asian ladybeetle, Harmonia axyridis (HA) by analyzing the microsatellite genetic variation among its populations worldwide. There have been repeated attempts to release H. axyridis as the biological control agent against aphids since early 1900s, but all failed. Since 1988, H. axyridis has been found unexpectedly in multiple areas. Some of these populations were eventually successful in the control of soybean aphids, but others became nuisance pests due to their unpleasant odors when they overwinter indoors in large numbers. A genetic study by Lombaert et al. (2010) showed that H. axyridis from its native Asia established its bridgehead in eastern U.S. in 1988, from which it was later introduced to South America, South Africa and Europe. The study of S. invicta invasive pathways to China offers another example of bridgehead effect (Yang et al. 2012). A comparison of the genetic variations among 27 populations of S. invicta (10 in China and 17 in the U.S.) showed that most populations in China appeared to have originated from Wuchuan in southwest Guangdong Province, P.R. China, in which this ant species first established, and served as the bridgehead population to other populations in China.


The process of successful establishment by invasive species as shown in Fig. 1 is part of a larger trend of “homogenocene” which was termed by Sam ways (1999) to characterize our current ecological era as an epoch with diminished biodiversity and increasing similarity among ecosystems worldwide. Homogenocene results from anthropogenic movement of organisms worldwide, and most attribute its beginning to the “Columbian Exchange,” i.e. the large scale exchange of goods, and macro- and microorganisms following the 1492 voyage of Christopher Columbus to the New World (Mann 2011). Connection of 2 once-separated Hemispheres prompted the movements of numerous organisms, but before the Columbian Exchange, there was another dramatic connection of 2 largely separated worlds during the Pax Mongolica via the Silk Road.

Pax Mongolica: 13th–14th Century

Following a series of wars waged through most of the 11th century, Genghis Khan and his descendents built the largest continuous empire in human history that stretched from the Pacific Ocean to the Caspian Sea and today's Moscow. The Mongol Empire was partitioned into 4 branches, and despite political tensions and constant squabbles among them, trade routes were kept open, and exchanges of goods, people, and ideas changed the lives of those inhabited within the Mongol Empire and the neighboring nations. The Silk Road (started in the Han dynasty, 206 BCE — 220 CE) was reopened as the main land route connecting China with Europe. The Maritime Silk Road connected China through SE Asia, the Indian Ocean, the Arabian Sea, the Persian Gulf, and the Red Sea to East Africa. Through these networks of trade routes, a global commerce flourished for the first time in human history, and productivity and populations of nations within the trade zone grew rapidly (Abu-Lughod 1989). The Yum system (a series of relay stations at every 32–40 km along the major routes to supply fresh horses and other travel accommodations) that was originally established to secure communication among Mongol troops, provided vital needs for traveling merchants, and the trade routes were manned by Mongol soldiers for safe passage. Chinese silk, exotic spices, Indian cotton, sugar and new crops such as carrots, turnips and buckwheat were introduced to Europe by merchants from the East.

In addition to commodities and products, people and information also flowed through the Silk Road. The Venetian merchant, Marco Polo traveled with his father and uncle to China (Cathay) and the book of his travel and adventure, “The Travel of Marco Polo” introduced Europeans to the exotic countries in the east, and stirred imagination of many including Christopher Columbus (Latham 1958). Introduction of Chinese innovations such as paper, printing, gunpowder, firearms and the magnetic compass were considered underlying factors for the emergence of Renaissance in Europe (Weatherford 2004). Through the same trade routes, the pathogen of Plague, the bacterium Yersinia pestis (Lehmann and Neumann 1896) van Loghem 1944, was also brought to Europe by its carrier, the Oriental rat flea, Xenopsylla cheopis (Rothschild) (Siphonaptera: Pulicidae) on rodents that hitchhiked trade ships from the Orient. The disease ravaged Asia with an estimated 25 million victims before entering Europe (Kohn 2008). Between 1347 and 1353, Plague killed one third of the European population, and profoundly altered the course of European history. The most significant impact of Pax Mongolica to homogenocene, however, is that stories of lands with abundance of gold, treasures, and exotic spices flowing through the Silk Road led Europeans to the age of discovery, and the Columbian Exchange.

Columbian Exchange

Columbus' voyage in 1492 connected 2 Hemispheres and promoted a dramatic and widespread exchange of organisms between them. New World crops such as maize, potato, tomato, tobacco, sweet potato, cacao, vanilla, pineapple, chili pepper, peanut, sunflower, and papaya were spread to and deeply affected lives of those in the Old World. Introduction of maize, potato and sweet potato to China, for example, turned marginal lands of mountainous terrains (which were unsuitable for cultivating traditional crops such as rice and wheat) into productive lands that contributed to the doubling of the Chinese population (Mann 2011) in the Qing dynasty (1644 to 1912). Potato was singularly responsible for the population explosion in Ireland as well as the Great Irish Famine (1845–1852) when the crops were decimated by potato blight. Before the 1500s, there were no tomatoes in Italian cuisine, no chocolate in Switzerland, no pineapples in Hawaii, no chili peppers in Thai or Indian food, no potatoes in the German diet, and no rubber trees in Malaysia. Almost as many plant species were also brought from the Old to New World, including apple, banana, black pepper, coffee, citrus, garlic, onion, peach, soybean, sugarcane, rice, wheat, and watermelon. Domesticated animals such as horse, chicken, donkey, pig, earthworm, honey bee and silkworm were introduced to the New World and changed the life style of Native Americans. As with Plague during the Pax Mongolica, many infectious diseases including malaria, small pox, chicken pox, cholera, leprosy, bubonic plague, yellow fever, typhoid, and measles were also brought from the Old to New World. Of these, the most devastating was small pox that killed 80–90% of Native American populations (Mann 2011). Columbus' crews who contracted syphilis spread it to European populations when some of them later joined the Spanish army to invade Italy. Edible plants and domestic animals were intentionally introduced, but diseases and other organisms were accidentally transferred, and many became invasive, e.g., brown rats, zebra mussels, tumbleweed (Salsola spp.; Caryophylalles: Amarantaceae), wild oat, and ascomycete microfungi (Ophiostoma spp.) responsible for Dutch elm disease. Some species such as Kudzu that was intentionally introduced (to prevent soil erosion) became a pest species, while others such as the yeast, Saccharomyces bayanus Saccardo, which was accidentally introduced from South America was later used for producing lager beer.


As shown in Fig. 1, propagule pressure is the major factor contributing to the increase of invasive species across the globe. Beginning with Pax Mongolica, and later the Columbian Exchange, anthropogenic movement of goods among major cities has increased over time, and this trend will only accelerate. This will heighten propagule pressure to provide more opportunities for potential invasive species, and to select for a more invasive population within a species. The number of invasive species, thus, will only increase for as long as current practices of global commercial activities continue. Between cities with heavy traffic, a more targeted quarantine/ inspection measure focusing on potential invasive species of the source region may be one solution to intercept their shipments and reduce propagule pressure.


I would like to thank P. Bardunias and A. Mullins (University of Florida) for review of the initial draft of this article.



J. L. Abu-Lughod 1989. Before European hegemony. The world system A.D. 1250–1350. Oxford University Press, New York, NY. 443 pp. Google Scholar


W. C. Allee 1931. Animal aggregation. A study in general sociology. University of Chicago Press, Chicago, IL. Google Scholar


W. C. Allee , and E. Bowen 1931. Study in animal aggregation: mass protection against colloidal silver among goldfishes. J. Exp. Zool. 61: 185–207. Google Scholar


Anonymous . 1999. Executive Order 13112 of February 3, 1999: Invasive Species. Federal Register 64: 6183– 6186. Google Scholar


R. I. Colautti , I. A. Grigorovich , and H. J. Macissac 2006. Propagule pressure: a null model for invasion. Biol. Invasions 8: 1023–1037. Google Scholar


J. H. Frank , and E. D. McCoy 1995. Introduction to insect behavioral ecology: The good, the bad, and the beautiful: Non-indigenous species in Florida. Invasive adventive insects and other organisms in Florida. Florida Entomol. 78: 1–15. Google Scholar


D. H. Habeck , and F. D. Bennett 1990. Cactoblastis cactorum Berg. (Lepidoptera: Pyralidae), a phycitine new to Florida. Florida Dept. Agric. Consum. Serv., Divn. Pl. Industry, Entomol. Circ. 333: 1–4. Google Scholar


G. C. Kohn 2008. Encyclopedia of plague and pestilence: from ancient times to the present. Infobase Publishing, New York, NY pp. 529. Google Scholar


C. S. Kolar , and D. M. Lodge 2001. Progress in invasion biology: predicting invaders. Trends in Ecology & Evolution, 16: 199–204. (doi:10.1016/S01695347(01)02101-2). Google Scholar


R. Latham 1958. The travels of Marco Polo. Penguin Books, London. 380 pp. Google Scholar


B. Leung , J. M. Drake , and D. M. Lodge 2004. Predicting invasions: propagule pressure and the gravity of Allee effects. Ecology 85: 1651–1660. Google Scholar


J. Lockwood , L. P. Cassey , and T. Blackburn 2005. The role of propagule pressure in explaining species invasions. Trends in Ecology & Evolution, 20: 223– 228(doi:10.1016/j.tree.2005.02.004) Google Scholar


E. Lombaert , T. Guillemaud , J-M. Cornuet , T. Malausa , and B. Facon 2010. Bridgehead effect in the worldwide invasion of the biocontrol harlequin ladybird. PLoS ONE 5: e9743 Google Scholar


C. C. Mann 2011. 1493. Uncovering the new world Columbus created. Alfred A. Knopf. New York, NY 2516 pp. Google Scholar


M. K. Rust , and N.-Y. Su 2012. Managing social insects of urban importance. Annu. Rev. Entomol. 57: 355–375 Google Scholar


M. Samways 1999. Translocating fauna to foreign lands: here comes the Homogenocene. J. Insect Conserv. 3: 65–66. Google Scholar


J. Weatherford 2004. Ghenghis Khan and the making of the modern world. Crown Publishers, New York, NY 312 pp. Google Scholar


C.-C. Yang , M. S. Ascunce , L.-Z. Luo , J.-G. Shao and C.-J. Shih 2012. Propagule pressure and colony social organization are associated with the successful invasion and rapid range expansion of fire ants in China. Mol. Ecol. 21: 817–833 Google Scholar
Nan-Yao Su "How to Become a Successful Invader," Florida Entomologist 96(3), 765-769, (1 September 2013).
Published: 1 September 2013
Columbian Exchange
efecto invasivo de la cabeza de puente
Intercambio Colombiano
invasive bridgehead effect
presión de propágulos
propagule pressure
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