Phragmites australis australis (Cav.) Trin. ex Steud.

Common Name: Common reed

Synonyms and Other Names:

Common reed, common reedgrass, giant reed, phrag, Arundo altissima Benth., Arundo australis Cav., Arundo graeca Link, Arundo isiaca Delile, Arundo maxima Forssk., Arundo occidentalis Sieber ex Schult., Arundo palustris Salisb., Arundo phragmites L., Arundo vulgaris Lam., Cynodon phragmites (L.) Raspail, Oxyanthe phragmites (L.) Nieuwl., Phragmites altissimus (Benth.) Mabille ex Debeaux, Phragmites australis var. berlandieri (E. Fourn.) C.F. Reed, Phragmites australis ssp. maximus (Forssk.) Soó, Phragmites berlandieri E. Fourn., Phragmites capensis Nees, Phragmites caudatus Nees ex Meyen, Phragmites chilensis Steud., 

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Identification: Introduced Phragmites australis subsp. australis is a perennial reed that grows from elongated rhizomes or stolons; 1-6 meters tall, forms dense stands which include both live and standing dead stems from previous year’s growth (Clayton et al. 2006, Klein 2011).

Leaves and Stems:

Culms (stems) erect; hollow; reed-like; simple; 150–600 cm long; 5-15 mm thick; hollow internodes (Clayton et al. 2006, Klein 2011). Culms are tan in color; ridged or ribbed; have a rougher texture than the native common reed (Swearingen and Saltonstall 2010).
Leaves are linear to lanceolate-linear; flat; drooping; leaf-blades deciduous at the ligule; 20–60 cm long; 8–32 mm wide with pointed tips (Clayton et al. 2006, Klein 2011). Leaf blade surface smooth; cauline (Clayton et al. 2006). Leaves are blue green and usually darker than the native lineage (Swearingen and Saltonstall 2010). Each leaf consists of a blade and a loose sheath separated ciliate ligules that form minute membranous rims fringed with hairs; 0.2-0.6 mm long (Clayton et al. 2006, Klein 2011). Leaf sheaths adhere tightly to culm throughout the growing season; persistent (Swearingen and Saltonstall 2010). Leaf-blade apex attenuates; filiform (Clayton et al. 2006).

Flower-head and Flowers:

Inflorescence a panicle; bearing juvenile spikelets at emergence (Clayton et al. 2006). Panicles are oblong, purplish when young, straw colored at maturity; 15-50 cm long; 6-20 cm wide (Clayton et al. 2006, Klein 2011). Primary panicle branches divided; bearing spikelets almost to the base Clayton et al. 2006). Spikelets solitary; pedicelled (Clayton et al. 2006). Pedicels are filiform (Clayton et al. 2006). Spikelets comprising 3–11 florets; with diminished florets at the apex (Clayton et al 2006, Klein 2011). Spikelets cuneate; laterally compressed; 10–18 mm long; stalked with 6-10 mm long hairs on the stalks; breaking up at maturity (Clayton et al. 2006). Floret callus elongated; 1–1.25 mm long; bearded; obtuse. Glumes are paired; persistent; shorter than spikelets; gaping (Clayton et al. 2006). Lower glume lanceolate; 3–7 mm long; 0.5–0.6 length of upper glume; membranous; without keels; 3–5 veined. Lower glume apex acute. Upper glume lanceolate; 5–10 mm long; without keels; 3–5 veined (Clayton et al. 2006, Klein 2011). Upper glume apex acute (Clayton et al. 2006). Basal florets are sterile florets are male with palea; persist on panicle (Clayton et al. 2006). Lemma are glabrous; lanceolate; 8–15 mm long; membranous; acuminate; with somewhat in-rolled margins. Lower lemmas are unawned and upper lemmas are awned; Lemma apex acuminate (Clayton et al, 2006, Klein 2011). Palea present; with scaberulous keels (Clayton et al. 2006). Flowers typically occur in August and September and form bushy panicles that are usually purple or golden in color with 2 lodicules, 3 anthers, and a glabrous ovary (Clayton et al. 2006, Klein 2011).

Fruit is a caryopsis with an adherent pericarp (Clayton et al. 2006). Seeds     are 2 to 3 mm long (Klein 2011). As seeds mature, the panicles begin to look “fluffy” due to the hairs in the spikelet on the rachilla, and they take on a grey sheen (Saltonstall 2005).

Other Features:

Below ground, Phragmites australis forms a dense network of roots and rhizomes which can go down up to two meters in depth to reach deep ground water (MA DCR 2002). The plant spreads horizontally by sending out underground rhizomes and over ground runners which can grow 10 or more feet in a single growing season if conditions are optimal (Swearingen and Saltonstall 2010).

Distinguishing Between Native and Non-native Phragmites australis:

Many morphological characteristics can be used to distinguish native Phragmites australis subsp. americanus from the introduced lineage Phragmites australis subsp. australis. However, there are many overlaps in characteristics making it necessary to look at multiple factors when making a determination based on morphology. The following characteristics should NOT be used to distinguish populations in southern areas (California to the Gulf of Mexico) where the Gulf coast type may be present as it is very similar in appearance to the introduced lineage (Swearingen and Saltonstall 2010).

Growth Forms:

Introduced Phragmites australis subsp. australis typically forms denser stands than the native Phragmites australis subsp. americanus, the introduced subspecies stands are also more likely to include dead stems from the previous year’s growth (MNFI 2016, Swearingen and Saltonstall 2010). Introduced Phragmites is more likely to form monocultures, outcompeting and excluding other plant species. The native Phragmites, is much less robust, typically occurring in low density stands, and is frequently found with other native plants but it can occasionally occur in very dense stands more typical of the introduced form when enriched with nutrients (MNFI 2016, Swearingen and Saltonstall 2010).


Leaves of the invasive subspecies are a bluish gray-green, while those of the native lineage are typically a lighter yellow-green (MNFI 2016, Swearingen and Saltonstall 2010). This is easiest to see when they grow side-by-side (MNFI 2016).

Leaf Sheaths:

The leaf sheaths of the introduced Phragmites adhere more tightly to the culm and persist as long as it remains standing, whereas those of the native lineage adhere less tightly and peel back eventually dropping off the culm once the leaf dies particularly at the lower nodes exposing the stem below (MNFI 2016, Swearingen and Saltonstall 2010).

Culms and Rhizomes:

Culms of the introduced lineage are rigid and have a rougher texture than the native, which is usually smooth and shiny (MNFI 2016). Culms of the native lineage are more likely to be red, typically around the nodes and where the leaf sheaths have been lost. Whereas the culms of the non-native lineage are usually a dull tan color (MNFI 2016). However, non-native Phragmites has stolons that can grow up to 50 feet or more in a season and may be red, also a little red may occasionally be seen on the culms of the introduced lineage but it is usually limited to lower nodes, which may lead to confusion (MNFI 2016, Swearingen and Saltonstall 2010). Little black spots are sometimes found on the culms of the native lineage, which are caused by a native fungus that has not yet adapted to the introduced form (Swearingen and Saltonstall 2010). The culms of the introduced form may have a sooty like mildew but it does not have the distinctive black fungal spots (Swearingen and Saltonstall 2010). Rhizomes of the native subspecies rarely exceed 15 mm in diameter and are a darker yellow than the introduced lineage (Swearingen and Saltonstall 2010).


The ligule of the introduced lineage is typically less than 1 mm (0.4-0.9 mm) in length. Ligules of the native are more than 1 mm (1-1.7 mm) (Swearingen and Saltonstall 2010). The native Phragmites is less sturdy and therefore its ligule is more likely to shred and fray by midsummer (MNFI 2016).


For the introduced lineage, the upper glume ranges in size from 4.5-7.5 mm, with most being <6 mm and the lower glume ranges in size from 2.5-5.0 mm, most being <4 mm; the native subspecies has an upper glume ranges in size from 5.5-11.5 mm, with most being >6 mm and lower glume is ranges in size from 3.5-6.5 mm, with most being >4 mm (Swearingen and Saltonstall 2010).


Introduced Phragmites is typically found in ditches, disturbed sites, and can tolerate saline habitats. In the Great Lakes basin, it is frequently found on shorelines (MNFI 2016). The native lineage is usually found in fens, sedge meadow, river banks and shores, and the Great Lake shores (MNFI 2016).

Growing Seasons:

Introduced Phragmites begins growing earlier in the season and continues later in the fall than does the native lineage (MNFI 2016).

Size: 2 to 6 meters in height

Native Range: Although the specific ephithet australis suggests it is native to Australia, it is believed that Phragmites australis subspe. australis originated from the Middle East (Swearingen and Saltonstall 2010). It now has a worldwide distribution and is considered native to Europe.

Great Lakes Nonindigenous Occurrences: Introduced Phragmites australis subspe. australis has a worldwide distribution and is abundant in many marsh communities and along the edges of lakes and rivers (Saltonstall 2002). Introduced to the east coast of the United States between late 1700s and early 1800s it has been gradually expanding westward (Swearingen and Saltonstall 2010). Genetic studies indicate that population of the introduced lineage probably come from Eurasia (Saltontstall 2002). Establishment and distribution have been correlated with human disturbances (Saltonstall 2002). Currently, it exists in all 49 mainland states in the United States, including Alaska (Klein 2011), as well as throughout southern portions of six Canadian provinces and is considered to be an indicator of wetland disturbance (Saltonstall 2002). In the United States it is most abundant along the Atlantic Coast and northeastern wetlands, however Midwest populations of Phragmites australis subsp. australis are escalating (IN DNR 2005). In the Great Lakes basin, it is frequently found on shorelines (MNFI 2016). It is also found throughout Europe, Asia, Africa, and Australia (IN DNR 2005). There is concern of range expansion north, because of warming trends due to global warming, which provide increased potential for seedling establishment (Brisson et al. 2008).

Distribution in Michigan is largely coastal with populations concentrated in the southeast and southwest corners of the state. It dominates the Saginaw Bay region, the St. Clair Delta, and to a lesser extent, in the northern tip of the lower peninsula and the eastern end of the upper peninsula (MNFI 2016).

Table 1. Great Lakes region nonindigenous occurrences, the earliest and latest observations in each state/province, and the tally and names of HUCs with observations†. Names and dates are hyperlinked to their relevant specimen records. The list of references for all nonindigenous occurrences of Phragmites australis australis are found here.

Full list of USGS occurrences

State/ProvinceFirst ObservedLast ObservedTotal HUCs with observations†HUCs with observations†
IL201020102Little Calumet-Galien; Pike-Root
IN201020104Little Calumet-Galien; St. Joseph; St. Joseph; St. Marys
MI1979202131Betsie-Platte; Betsy-Chocolay; Black-Presque Isle; Boardman-Charlevoix; Brule; Cheboygan; Clinton; Detroit; Fishdam-Sturgeon; Huron; Kalamazoo; Keweenaw Peninsula; Lake Huron; Lake St. Clair; Lake Superior; Lower Grand; Manistee; Manistique River; Muskegon; Ontonagon; Ottawa-Stony; Pigeon-Wiscoggin; Raisin; Saginaw; Shiawassee; St. Clair; St. Joseph; St. Joseph; Thunder Bay; Tittabawassee; Upper Grand
MN200920214Baptism-Brule; Beartrap-Nemadji; Lake Superior; St. Louis
NY1991202212Black; Buffalo-Eighteenmile; Chaumont-Perch; Grass; Irondequoit-Ninemile; Lake Erie; Lower Genesee; Niagara River; Oak Orchard-Twelvemile; Oneida; Salmon-Sandy; Seneca
OH2004202213Ashtabula-Chagrin; Auglaize; Black-Rocky; Blanchard; Cedar-Portage; Cuyahoga; Grand; Huron-Vermilion; Lake Erie; Lower Maumee; Ottawa-Stony; Sandusky; Tiffin
PA182820101Lake Erie
WI1938202314Bad-Montreal; Beartrap-Nemadji; Door-Kewaunee; Lake Superior; Lake Winnebago; Lower Fox; Manitowoc-Sheboygan; Menominee; Milwaukee; Oconto; Peshtigo; St. Louis; Upper Fox; Wolf

Table last updated 7/14/2024

† Populations may not be currently present.

Ecology: Habitat:

Phragmites australis subsp. australis is a hardy species that can survive and proliferate in a wide range of environmental conditions, but prefers the wetland-upland interface (Avers et al. 2014). It grows on most soil textures from fine clay to sandy loams and is somewhat tolerant of saline or alkaline conditions (ISSG 2011) and so it is often found at the upper edges of estuaries and on other wetlands (such as grazing marshes) that are occasionally inundated by the sea. It is most often found on disturbed sites with altered hydrology, sedimentation, and nutrient enrichment. The United States Department of Agriculture, Natural Resources Conservation Service (USDA, NRCS) has designated Phragmites australis to be a 'FACW', which is roughly equivalent to a 75% chance of this plant occurring in wetlands (USDA, NRCS 2016). Phragmites can tolerate anoxic conditions, and high salinity in soils, and a wide range of pH from 3.9-8.6 (Fofonoff et al. 2015). Phragmites can also tolerate a wide range of temperatures, but shoots are killed off by severe frost events (Haslam 1972). Below ground, introduced Phragmites forms a dense network of roots and rhizomes that can extend downward over a meter (Swearingen and Saltonstall 2010). Along rivers and coastal shorelines, fragments of rhizomes transported from distant infested sites can settle in new spots and become rooted (Swearingen and Saltonstall 2010). Rhizome fragments may also be moved by heavy machinery (Swearingen and Saltonstall 2010).

Age and Growth:

Introduced Phragmites has an average lifetime of 4.5 years, but may live up to 6 years, when longevity is defined as the lifetime of an individual rhizome, but due to its clonal growth abilities, stands have been known to survive for 1000’s of years (Haslam 1972). Vegetative spread by below-ground rhizomes can result in dense stands that have more than 200 shoots/m2 (Haslam 1972).


Introduced Phragmites australis reproduces primarily clonally through the production and fragmentation of underground rhizomes, but is capable of sexual reproduction through seeds (Fofonoff et al. 2015). Phragmites is wind-pollinated; cross pollination with other plants is probably most common, but self-pollination or agamospermy may occur (Gucker 2008). Flowering starts in late July (Fofonoff et al. 2016). Seeds are primarily dispersed by wind in the fall and winter months (Fofonoff et al. 2015, Haslem 1972). However, they can also be transported on birds, or by water, via waterways or by flooding (Haslam 1972). Seed set is highly variable, with germination rates that are typically low (Haslam 1972), though mature plants may produce as many as 2,000 seeds annually (Avers et al. 2014). Some sources have even reported as many as 1000 seeds per every inflorescence (Haslam 1972). Local propagation is largely to be considered achieved through vegetative reproduction with seeds responsible for new colonization events (Mark et al. 1994). Plants growing in harsh environments may not be able to flower, so the only mode of reproduction is vegetative (Haslam 1972). Germination takes place on exposed moist soils in spring, at temperatures above 10 C (March-April) (Fofonoff et al. 2015). Water depths greater than 5 cm (2 in) generally prevent germination (Marks et al. 1994). After germination a rhizome takes 2-4 years to flower for the first time (Haslam 1971).

Great Lakes Means of Introduction: Initial introduction to the United States was likely via solid ballast and/or packing material from shipping (Swearingen and Saltonstall, 2010). Phragmites has been intentionally introduced to some locations as a filter plant in wastewater treatment lagoons and has been used for erosion control and as a tool to stabilize shorelines (IN DNR, 2016).

Along rivers and coastal shorelines, fragments of rhizomes transported from distant infested sites can settle in new spots and become rooted (Swearingen and Saltonstall, 2010). Rhizome fragments may also be moved by heavy machinery (Swearingen and Saltonstall, 2010).

Great Lakes Status: Overwintering and reproducing with widespread self-sustaining populations in all 5 Great Lakes basins.

Great Lakes Impacts:
Summary of species impacts derived from literature review. Click on an icon to find out more...


Phragmites australis has a high environmental impact in the Great Lakes.

The leaves and stems of Phragmites have poor nutritional value and few organisms feed on it in North America, so replacement of native vegetation by the less nutritious Phragmites could have negative consequences for herbivores (Great Lakes Phragmites Collaborative 2023). Larval and juvenile fish seem to be the most negatively affected by Phragmites (Great Lakes Phragmites Collaborative 2023). The species produces abundant litter which can reduce the mobility of juvenile fish.

Phragmites displaces native plant species including sedges, rushes, and cattails; and reduces wildlife habitat diversity, resulting in loss of food and shelter for native wildlife (Avers et al. 2010). In Ontario, Canada, Blanding Turtles (Emydoidea blandingii) avoided nesting in Phragmites  patches thus reducing the amount of suitable nesting habitat available in an invaded marsh areas (Markle and Chow-Fraser, 2018). Its success may also be attributed to allelopathy; Phragmites releases gallic acid, which is degraded by ultraviolet light to produce mesoxalic acid, exposing susceptible plants and seedlings with two harmful toxins (Rudrappa 2009). Furthermore, Phragmites alters wetland hydrology through increased evaporation and trapping of sediments, causing marsh soils to dry out (Avers et al. 2010, Swearingen and Saltonstall 2010). Phragmites also impacts nutrient levels; when meadow marsh were replaced with Phragmites in Long Point peninsula, Ontario, Canada, the stocks of Ca, P, K, N, Mg, and C all increased significantly with a mean increase ranging from 103-188% (Yickin and Rooney, 2019).

Phragmites australis has a moderate socio-economic impact in the Great Lakes.

Tall, dense stands of the introduced Phragmites impede shore access, as penetration of a stand of introduced Phragmites can not only be difficult but can also result in abrasions from the sharp-edged vegetation (Avers et al., 2010, USFWS, 2007). Recreational value for birdwatchers, walkers, naturalists, boaters, and hunters is further diminished through reduction of native fish and wildlife populations (USFWS 2007). Such use impairment and restricted shoreline view also reduce property values (Avers et al. 2010).

In addition to economic impacts, the introduced Phragmites poses a risk to human life and property. The Michigan Department of Transportation (MDOT) considers Phragmites to be a safety hazard, as its height and dense growth may block signs and view of access roads, drives, curves, etc. (B. Batt, MDOT, pers. comm.). During its dormant season, when dry biomass is high, the introduced common reed also creates a potentially serious fire hazard to structures (Avers et al., 2010, Swearingen and Saltonstall 2010).

Phragmites australis has a high beneficial effect in the Great Lakes.

As a wetland plant, Phragmites improves water quality by filtration and nutrient removal (Ailstock, 2004). Phragmites provides food and habitat for some organisms and serves to stabilize soils against erosion. Bobolink and sparrows eat its seeds, while numerous insects eat the vegetation. Moreover, many insects, birds (including yellowthroat, marsh wren, salt marsh sparrow, least bittern, red-winged blackbird, and some wading birds), and muskrats use Phragmites as shelter or nest material (Kiviat, 2010).

Remarks: Recent research suggests that at least 3 types of Phragmites australis are present in the United States (Swearingen and Saltonstall 2010). The North American native type of Phragmites australis has been designated as a separate subspecies: Phragmites australis subsp. americanus. A second genetic type designated as the ‘Gulf’ type is native to Mexico and Central America and cryptogenic to the southern U.S., but it is clearly spreading along the southern tier of states. The Gulf type has been designated as Phragmites australis subsp. berlandieri (Saltonstall and Hauber 2007), but this proposed taxonomy remains unaccepted. The European ‘introduced lineage’, which is the focus of this factsheet, may represent a single or multiple subspecies. This introduced lineage is sometimes designated as Phragmites australis subsp. australis, but this is not an officially recognized subspecies name. Other authors refer to the introduced lineage as haplotype M.

Other synonyms: Phragmites communis Trin., Phragmites communis var. berlandieri (E. Fourn.) Fernald, Phragmites communis ssp. berlandieri (E. Fourn.) Á. Löve & D. Löve, Phragmites communis var. flavescens Custer, Phragmites communis var. genuinus Stuck., Phragmites communis var. hispanicus (Nees) K. Richt., Phragmites communis var. isiacus (Delile) Engl., Phragmites communis var. mauritianus (Kunth) Baker, Phragmites communis ssp. maximus (Forssk.) Clayton, Phragmites communis var. variegatus Hitchc. ex L.H. Bailey, Phragmites dioicus Hack. ex Conert, Phragmites dioicus Hack. ex Hicken, Phragmites fissifolius Steud., Phragmites hispanicus Nees, Phragmites isiacus (Delile) Kunth, Phragmites martinicensis Trin. ex Steud., Phragmites mauritianus Kunth, Phragmites maximus (Forssk.) Chiov., Phragmites maximus var. berlandieri (E. Fourn.) Moldenke, Phragmites maximus var. variegatus (Hitchc. ex L.H. Bailey) Moldenke, Phragmites occidentalis Trin. ex Steud., Phragmites phragmites (L.) Speg., Phragmites phragmites (L.) H. Karst., Phragmites vulgaris (Lam.) Crép., Phragmites vulgaris Britton, Sterns & Poggenb., Phragmites vulgaris var. mauritianus (Kunth) T. Durand & Schinz, Phragmites vulgaris ssp. maximus (Forssk.) Chiov., Reimaria diffusa Spreng., Trichoon phragmites (L.) Rendle

References (click for full reference list)

Author: Sturtevant, R., A. Fusaro, W. Conard, S. Iott, L. Wishahm and J. Van Zeghbroeck

Contributing Agencies:

Revision Date: 1/19/2024

Citation for this information:
Sturtevant, R., A. Fusaro, W. Conard, S. Iott, L. Wishahm and J. Van Zeghbroeck, 2024, Phragmites australis australis (Cav.) Trin. ex Steud.: U.S. Geological Survey, Nonindigenous Aquatic Species Database, Gainesville, FL, and NOAA Great Lakes Aquatic Nonindigenous Species Information System, Ann Arbor, MI,, Revision Date: 1/19/2024, Access Date: 7/14/2024

This information is preliminary or provisional and is subject to revision. It is being provided to meet the need for timely best science. The information has not received final approval by the U.S. Geological Survey (USGS) and is provided on the condition that neither the USGS nor the U.S. Government shall be held liable for any damages resulting from the authorized or unauthorized use of the information.