Cryptic invasion by a non-native genotype of the common reed, Phragmites australis, into North America

By K. Saltonstall. Proceedings of the National Academy of Sciences of the United States of America, 2002

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Citations in the corpus

Nitrogen Uptake by Native and Invasive Temperate Coastal Macrophytes: Importance of Dissolved Organic Nitrogen (2010, background): “2004), and at the same time, introduced Phragmites has outcompeted the native type (Saltonstall 2002), and has expanded into historically unoccupied habitats throughout North American wetlands (Chambers et al.”
Host range of Tetramesa romana Walker (Hymenoptera: Eurytomidae), a potential biological control of giant reed, Arundo donax L. in North America (2009, background): “There is only one Phragmites species present in N. America (P. australis), but there is a considerable body of knowledge associated with P. australis because of its worldwide distribution and invasiveness in northeastern N. America (Saltonstall, 2002).”
DIEL MINERALIZATION PATTERNS OF STANDING-DEAD PLANT LITTER: IMPLICATIONS FOR CO2 FLUX FROM WETLANDS (2004, background): “Furthermore, P. australis is aggressively invading both freshwater and salt marshes in North America, where it replaces native wetland vegetation such as cattail and cordgrass (Findlay et al. 2002, Saltonstall 2002).”
Detecting local adaptation in widespread grassland species – the importance of scale and local plant community (2006, background): “In Phragmites australis, a superior foreign genotype seems to be invading many natural sites in North America displacing local genotypes of this species (Saltonstall 2002).”
Higher genetic diversity in introduced than in native populations of the mussel Mytella charruana: evidence of population admixture at introduction sites (2009, neutral): “Patterns of genetic variation have proven indispensable for determining the likely source of a founding population (Saltonstall, 2002; Taylor & Keller, 2007; Le Roux & Wieczorek, 2009; but see Muirhead et al., 2008).”
Seeds contribute strongly to the spread of the invasive genotype of the common reed (Phragmites australis) (2010, methodology): “However, the swiftness of the spread of the haplotype M in North America (Saltonstall 2002; Lelong et al. 2007), and the rapid rise in the number of common reed stands in sites that have recently been invaded (Hudon et al.”
Causes and Consequences of Invasive Plants in Wetlands: Opportunities, Opportunists, and Outcomes (2004, background): “One population of Phragmites australis that invaded a wetland along Lake Superior was hypothesized to be exotic, but genetic analysis proved it to belong to the native strain (Lynch and Saltonstall, 2002).”
Identification of exotic sailfin catfish species (Pterygoplichthys, Loricariidae) in Taiwan based on morphology and mtDNA sequences. (2011, background): “Another case occurred when a non-native genotype invaded native reeds (Phragmites australis), and caused a dramatic increase of the population in the last 150 yr (Saltonstall 2002).”
Centuries of human-driven change in salt marsh ecosystems. (2009, background): “An aggressive, European P. australis haplotype has increased in abundance in North American marshes over the past century, outcompeting native plants (Minchinton et al. 2006, Orson 1999, Saltonstall 2002).”
Application of genetic diversity–ecosystem function research to ecological restoration (2014, background): “could potentially become invasive is extremely problematic (e.g. Phragmites australis; Saltonstall 2002), in part because such cryptic invaders would be nearly impossible”
Deep Invasion Ecology and the Assembly of Communities in Historical Time (2009, background): “australis (Saltonstall 2002).”
Plant functional group identity and diversity determine biotic resistance to invasion by an exotic grass (2013, background): “…invasiveness (Vellend, Drummond & Tomimatsu 2010; Drummond & Vellend 2012), and currently three distinct lineages of P. australis are recognized in North America, including one of Eurasian origin (principally haplotype M, Saltonstall 2002), which is widely distributed and invasive in many regions.”
Genetic diversity patterns in Phragmites australis at the population, regional and continental scales (2008, background): “…of the efficiency of the dispersal of P. australis are its virtually cosmopolitan distribution, its occurrence in isolated patches of suitable habitat such as oceanic islands (Saltonstall, 2002), and its presence in nearly every lake, pond, river, and marsh in the northern temperate zone.”
Implications and future prospects for evolutionary analyses of DNA in historical herbarium collections (2018, background): “For example, Saltonstall (2002) sequenced chloroplast markers from historical herbarium specimens of the reed Phragmites australis (Cav.)”
Tracking biological invasions in space and time: elucidating the invasive history of the green alga Codium fragile using old DNA (2007, positive): “There are, however, notable exceptions to this: a study into the invasive history of the weed Phragmites australis utilized 62 herbarium samples covering the majority of the USA and was able to track the spread of introduced haplotypes before and after 1910 (Saltonstall, 2002).”
How did common ragweed (Ambrosia artemisiifolia L.) spread in Québec? A historical analysis using herbarium records (2007, methodology): “Saltonstall (2002) used molecular techniques to distinguish native and exotic genotypes of common reed [Phragmites australis (Cav.)”
Expansion pathways of the exotic common reed (Phragmites australis): a historical and genetic analysis (2007, methodology): “On the other hand, using DNA sequencing, Saltonstall (2002) showed that the North American invasion by the common reed coincided with the introduction of an exotic genotype (haplotype M) along the eastern coast of North America.”