Typha domingensis

Pers.

Southern Cattail

G4Apparently Secure (G4G5) Found in 10 roadless areas NatureServe Explorer →
G4Apparently SecureGlobal Rank
Least concernIUCN
Identity
Unique IDELEMENT_GLOBAL.2.144988
Element CodePMTYP01030
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomPlantae
PhylumAnthophyta
ClassMonocotyledoneae
OrderTyphales
FamilyTyphaceae
GenusTypha
Other Common Names
southern cattail (EN)
Concept Reference
Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Conservation Status
Review Date1985-10-24
Change Date1985-10-24
Edition Date1987-10-27
Edition AuthorsK. MOTIVANS, S. APFELBAUM, MRO
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Rank Reasons
Wide distribution range in the U.S.
Range Extent Comments
Typha domingensis has a range which extends from the southwest United States, southern California and east to southeastern Virginia.
Threat Impact Comments
Cattail management may be desired in situations where cattails have responded to wetland disturbance by growing in dense monocultures. The genus Typha can behave like aggressive introduced weeds in a variety of natural communities throughout North America (Apfelbaum 1985). Cattails are considered serious weeds in some countries (Holm et al. 1979, Morton 1975) but not necessarily in North America.

In high-quality natural communities, cattails usually occur as scattered sterile plants (Apfelbaum 1985). With disruptions to a community, cattail populations may respond by spreading vegetatively at a rapid rate. The effect of the growth spurt is closing open water, eliminating habitat and species diversity, and reducing the opportunity for other plants to become established and survive. Shading is a significant effect on other plants. Cattails are successful because they form extensive monocultures very rapidly through vegetative reproduction and maintain their dominance with the formation of dense rhizomes mats and litter.

Cattails have a wide ecological amplitude compared to other species (Pianka 1973). They are tolerant to habitat changes, pollutants in the water system, and saline or basic substrates. A study in Indiana concluded that the three basic events precede the growth of cattails monocultures: 1. modified surface hydrology, 2. wildfire suppression, and 3. wetland enrichment (Wilcox et al. 1984). Claims that hybrid cattails are responsible for monoculture growths have not been confirmed.
Ecology & Habitat

Diagnostic Characteristics

The tall cattail (Typha domingensis) may be difficult to separate from T. angustifolia. T. domingensis is usually taller and has flattened and more numerous leaves (Apfelbaum 1985). Hybrids of intermediate appearance have been reported, and are often referred to as the species Typha x glauca.

Habitat

Cattails have a cosmopolitan distribution and a wide ecological amplitude. Typha can be found in wetlands, sedge meadows, along slow moving streams, river banks, and lake shores. The plant is found in areas of widely fluctuating water levels such as roadside ditches, reservoirs and other disturbed wet soil areas. Cattails commonly invade the pelagic zones of bogs (Gustafson 1976). Typical associates include Phragmites australiis, Lythrum salicaria, Spartina sp., Acorus calamus, Scirpus sp., and Sagittaria latifolia. T. domingensis and T. angustifolia are restricted to less favorable and more saline habitats when they occur with T. latifolia, which competes against other cattail species (Gustafson 1976).

Cattails can grow on a wide gradient of substrate types. Wet pure sand, peat, clay and loamy soils have been documented under cattail stands. World wide distribution of cattails is summarized by Morton (1975).

Ecology

The structure of cattail stands as it is, with upright leaves, high leaf area, balanced horizontal and vertical distribution of leaf area and shifts in leaf angle are all factors which permit monoculture success. An open, generously sunny habitat and abundant moisture can provide the setting for maximum cattail production.

Typha plants are mined by caterpillars of the moths Arzama opbliqua and Nonagria oblonga (Klots 1966). Aphids and Colandra pertinaux (the snout beetle) also feed on Typha leaves and stems. The stems may have many species of pupa living within them (Klots 1966). The cattail rhizomes provide food to mammals such as the muskrat. The grazing of muskrats may greatly influence cattail communities. A cycling population of muskrats may reach such a density so as to totally set back a cattail stand for the season. These "eat outs" are important to maintain open water in a balanced system. Muskrats utilize leaves and stems for houses and eat the rhizomes (Zimmerman pers. comm.). Cattail fruits provide nesting material for terrestrial birds and dry stems may be used by aquatic birds.

Above ground portions die in the late fall and rhizomes overwinter. In Wisconsin, it was found that average winter marsh temperatures greater then 8 degrees C reduced carbohydrate reserves in Typha latifolia to an extent sufficient to inhibit shoot growth in the spring (Adriano et al. 1980). Cattail population success has been correlated with nutrient fertility (Boyd 1971), water level and substrate temperature (Adriano et al. 1980).

The plant tissues can store relatively high concentrations of some metals. Typha appears to have an internal copper and nickel tolerance mechanism. It is not likely that there is an evolutionary selection for heavy metal tolerance, but rather it is inherent in the species (Taylor and Crowder 1984).

Reproduction

Cattails flower in late May and June and sometimes later (up to late July) depending, perhaps, on soil and water temperatures as influenced by climate and litter in a stand. The wind-borne pollen attaches to stigmas of female florets to eventually produce achene fruits. The elongated embryo and stalk are covered with fine, unmatted hairs that aid in wind dispersal. Fruits are mature in August and September. Seeds are very small, weighing 0.055 mg each (Keddy and Ellis 1985).

Many cattail germination studies have been conducted. Some of these suggest that germination requirements are few. Seed germination can be 100 percent in slightly flooded conditions (Smith 1967). Other studies have confirmed that water is required at a depth of 2.54 cm for germination.

Van der Valk and Davis (1976) suggested that the germination of Typha seeds could be inhibited by an allelopathic interaction caused by Typha litter. Seed longevity and dormancy may be affected by soil moisture, temperature and soil atmosphere (Schafer and Chilcote 1970, Roberts 1972, Meyer and Poljakoff-Mayber 1963, Morinaga 1926).

Young Typha shoots grow rapidly from seeds in favorable substrates. Cattail colonies are commonly maintained by vegetative reproduction. A perennial root stock is the major organ responsible for reproduction (Apfelbaum 1985). Cattail productivity has been well documented. Net annual production has usually been estimated as the maximum standing crop (shoot biomass) values for a good site are generally between 1000 and 1700 g/m (d.w.) (Gustafson 1976). Figures for Typha production mostly exceed the average standing crop yields for maize and sorghum.

Shoot density reports (numbers of stems per square meter) range from 28/m2 (Curtis 1959) in Wisconsin to an extreme example reported by Dykyjova, et al. (1971) of 108/m2. In a greenhouse experiment, ninety-eight vegetative shoots and 104 crown buds were produced on a single seedling during it's first year (Timmons et al. 1963). Cattails can produce 20,000-700,000 fruits per inflorescence (Prunster 1941, Marsh 1962, Yeo 1964). Vegetative growth by broad-leaved cattails of 518 cm (17 feet) annually have been recorded (McDonald 1951), and plants grown from seed flowered the second year (Smith 1967, Yeo 1964).

Cattail plants produce a dense rhizome mat and the clustered leaves produce a thick litter layer. Dense cattail growth and litter may reduce the opportunity for other plants to establish or survive (Wesson and Waring 1969).
Palustrine Habitats
HERBACEOUS WETLANDBog/fen
Other Nations (1)
United StatesNNR
ProvinceRankNative
ArizonaSNRYes
NevadaS3Yes
TennesseeSNRYes
North CarolinaS3Yes
VirginiaS3Yes
UtahSNRYes
OregonSNRYes
NebraskaSNANo
New MexicoSNRYes
LouisianaSNRYes
ArkansasSNRYes
South CarolinaSNRYes
IndianaSNANo
MarylandS3Yes
GeorgiaSNRYes
AlabamaSNRYes
MississippiSNRYes
TexasSNRYes
FloridaS4Yes
HawaiiSNANo
KansasS4Yes
CaliforniaSNRYes
WyomingS1Yes
OklahomaSNRYes
MissouriS1Yes
ColoradoS3Yes
Plant Characteristics
DurationPERENNIAL, SPRING-FLOWERING, SUMMER-FLOWERING
Economic Value (Genus)No
Roadless Areas (10)
Arizona (3)
AreaForestAcres
Black CrossTonto National Forest5,966
GoldfieldTonto National Forest15,257
Lime CreekTonto National Forest42,568
California (5)
AreaForestAcres
Eagle PeakCleveland National Forest6,481
LaddCleveland National Forest5,300
No NameCleveland National Forest4,897
Pine CreekCleveland National Forest503
Red MountainAngeles National Forest8,034
Nevada (2)
AreaForestAcres
Antelope - West 1Humboldt-Toiyabe National Forest8,642
Table Mtn. - EastHumboldt-Toiyabe National Forest87,789
References (2)
  1. Flora of North America Editorial Committee (FNA). 2000. Flora of North America north of Mexico. Vol. 22. Magnoliophyta: Alismatidae, Arecidae, Commelinidae (in part), and Zingiberidae. Oxford Univ. Press, New York. xxiii + 352 pp.
  2. Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.