Typha latifolia

L.

Broadleaf Cattail

G5Secure Found in 64 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
UnknownThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.153503
Element CodePMTYP01040
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
broadleaf cattail (EN) Quenouille à feuilles larges (FR)
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
Rank Method Rank calculation - Biotics v2
Review Date2024-07-09
Change Date1984-09-06
Edition Date2024-07-09
Edition AuthorsK. MOTIVANS, S. APFELBAUM, MRO, rev. Eberly (2024)
Threat ImpactUnknown
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences> 300
Rank Reasons
Typha latifolia is a cosmopolitan emergent, aquatic perennial herb. With a large range extent, thousands of occurrences, abundant habitat, broad habitat preferences, and no obvious intrinsic vulnerabilities, this species is considered secure
Range Extent Comments
Typha angustifolia is a cosmopolitan species that is found extensively throughout the Northern Hemisphere but more sporadic across the southern hemisphere.
Occurrences Comments
By applying a 1 km separation distance to herbarium records and photo-based observations documented between 1993 and 2024, there are estimated to be thousands of occurrences rangewide (GBIF 2024, iNaturalist 2024, SEINet 2024).
Ecology & Habitat

Diagnostic Characteristics

Typha latifolia, Broad-leaved Cattail, is distinguished from T. angustifolia, Narrow-leaved Cattail, by the relative width of the leaf and the position of the staminate and pistillate portions of the spadix (heads). Typha latifolia has 6-23 mm wide leaves that are flat, sheathing, and pale grayish-green in color. Typha angustifolia has 3-8 mm wide leaves that are full green and somewhat convex on back (USDA 1971). In T. latifolia the staminate and pistillate heads are contiguous or nearly so, whereas in T. angustifolia the heads are separated by approximately 3 cm.

Cattail fruits differ among the two major species. Typha angustifolia fruits are about 5-8 mm long with hairs arising above the middle. Typha latifolia fruits are about 1 cm long with hairs arising near the base (USDA 1971).

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. They can grow on a wide gradient of substrate types: wet pure sand, peat, clay and loamy soils. 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 australis, Lythrum salicaria, Spartina spp., Acorus calamus, Scirpus spp., and Sagittaria latifolia.

Typha angustifolia is widely distributed in the eastern and northern United States and is generally restricted to unstable environments, often with basic, calcareous, or somewhat salty soils (Fassett and Calhoun 1952). Narrow-leaved cattail can grow in deeper water compared to T. latifolia, although both species reach maximum growth at a water depth of 50 cm (20 inches) (Grace and Wetzel 1981). A robust hybrid between narrow-leaved and broad-leaved cattail, Typha x glauca, has similar habitat requirements to T. angustifolia.

Typha latifolia is found in the most favorable sites where it competes against other species. T. angustifolia and T. domingensis are restricted to less favorable and more saline habitats when they occur with T. latifolia (Gustafson 1976). Typha latifolia often displaces T. angustifolia in shallow (<15 cm) water, restricting the latter species to deep water (Grace and Wetzel 1981). Typha angustifolia is considered a pioneer in secondary succession of disturbed bogs (Wilcox et al. 1984). Presumably, an increase in the acidity of a bog would lower the pH and reduce the invasion of T. angustifolia. Theodore Cochran (pers. comm), of the University of Wisconsin-Madison herbarium states that most early herbarium specimens are T. latifolia and only recently have T. angustifolia specimens been collected from Wisconsin wetlands.

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). Typha latifolia seeds are less tolerant to salt (NaCl) concentrations in the substrate when compared to T. angustifolia seeds. However, seeds of both species which had been soaked in salt solution would germinate after being returned to non-saline conditions (McMillan 1959). Typha angustifolia seeds showed no significant germination response when sprouted along a moisture gradient which ranged from 5 cm below substrate to 10 cm above (Keddy and Ellis 1985). Other studies have confirmed that water is required at a depth of 2.54 cm for germination. Sifton (1959) showed light and low oxygen tensions affected germination of broad-leaved cattail.

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 (2)
CanadaN5
ProvinceRankNative
SaskatchewanS4Yes
ManitobaS4Yes
Yukon TerritoryS4Yes
QuebecS5Yes
OntarioS5Yes
AlbertaS5Yes
Nova ScotiaS5Yes
Prince Edward IslandS5Yes
Northwest TerritoriesS4Yes
NunavutSUYes
New BrunswickS5Yes
British ColumbiaS5Yes
United StatesN5
ProvinceRankNative
GeorgiaSNRYes
North DakotaSNRYes
LouisianaSNRYes
MinnesotaSNRYes
OhioSNRYes
VermontS5Yes
MarylandSNRYes
ConnecticutSNRYes
IndianaSNRYes
TennesseeSNRYes
North CarolinaS5Yes
IllinoisS5Yes
New HampshireSNRYes
IdahoSNRYes
WyomingS4Yes
MontanaS5Yes
NebraskaSNRYes
South DakotaSNRYes
CaliforniaSNRYes
IowaS5Yes
PennsylvaniaS5Yes
New MexicoSNRYes
KansasS5Yes
MaineSNRYes
NevadaS3Yes
South CarolinaS5Yes
FloridaS5Yes
West VirginiaS5Yes
MichiganSNRYes
OklahomaSNRYes
VirginiaS5Yes
MassachusettsSNRYes
TexasSNRYes
ColoradoS4Yes
WashingtonSNRYes
District of ColumbiaS5Yes
New JerseyS5Yes
ArizonaSNRYes
DelawareS5Yes
KentuckyS5Yes
UtahSNRYes
ArkansasSNRYes
AlaskaSNRYes
Rhode IslandSNRYes
AlabamaSNRYes
OregonSNRYes
WisconsinSNRYes
MissouriSNRYes
HawaiiSNANo
MississippiSNRYes
New YorkS5Yes
Threat Assessments
ThreatScopeSeverityTiming
Unknown/undetermined

Plant Characteristics
DurationPERENNIAL, SPRING-FLOWERING, SUMMER-FLOWERING
Economic Value (Genus)No
Roadless Areas (64)
Alaska (6)
AreaForestAcres
Boston BarChugach National Forest53,617
Chugach-13Chugach National Forest13,337
Copper River WetlandsChugach National Forest85,972
Fidalgo-GravinaChugach National Forest257,968
ResurrectionChugach National Forest224,615
Sheridan GlacierChugach National Forest224,683
California (8)
AreaForestAcres
Black ButteMendocino National Forest15,461
Cucamonga CSan Bernardino National Forest4,106
GrindstoneMendocino National Forest26,031
Horse Creek RidgeSan Bernardino National Forest8,969
Middle ForkPlumas National Forest29,278
Mt. Shasta BShasta-Trinity National Forest2,809
Raywood Flat BSan Bernardino National Forest11,373
Strawberry PeakAngeles National Forest7,245
Colorado (2)
AreaForestAcres
HermosaSan Juan NF148,103
Long ParkRoutt NF42,100
Idaho (5)
AreaForestAcres
HoodooNez Perce-Clearwater National Forest153,868
Italian PeakCaribou-Targhee National Forest141,158
NeedlesPayette National Forest131,279
Pioneer MountainsSawtooth National Forest119,563
Pioneer MountainsSalmon-Challis National Forest172,460
Michigan (1)
AreaForestAcres
Norwich Plains Revised Roadless AreaOttawa National Forest4,360
Minnesota (2)
AreaForestAcres
Cabin CreekSuperior National Forest6,071
Phantom LakeSuperior National Forest6,521
Montana (12)
AreaForestAcres
Bear - Marshall - Scapegoat - SwanLewis and Clark National Forest344,022
Bear - Marshall - Scapegoat - SwanLolo National Forest118,485
Bmss Ra 1485Flathead National Forest334,275
BridgerGallatin National Forest45,059
Cabinet Face East #671Kootenai National Forest50,326
East PioneerBeaverhead-Deerlodge National Forest145,082
Mt. Gmt Area HCuster National Forest1,335
North AbsarokaCuster National Forest21,063
Reservation DivideLolo National Forest16,908
Selway - Bitterroot (01067)Bitterroot National Forest114,953
Silver KingLolo National Forest12,816
West Big HoleBeaverhead-Deerlodge National Forest133,563
Nevada (2)
AreaForestAcres
Pearl PeakHumboldt-Toiyabe National Forest71,405
Ruby - Lamoille CynHumboldt-Toiyabe National Forest32,771
New Hampshire (1)
AreaForestAcres
Sandwich RangeWhite Mountain National Forest16,797
New Mexico (2)
AreaForestAcres
Canjilon Mtn.Carson National Forest7,972
Nichols ReservoirSanta Fe National Forest1,518
Oregon (8)
AreaForestAcres
Crane MountainFremont National Forest23,096
Dixie ButteMalheur National Forest12,208
Echo MountainWillamette National Forest8,098
Hurricane CreekWallowa-Whitman National Forest1,606
Mt. BaileyUmpqua National Forest18,401
Roaring RiverMt. Hood National Forest27,316
Salmon - HuckleberryMt. Hood National Forest17,570
TahkenitchSiuslaw National Forest5,799
Utah (4)
AreaForestAcres
418025Uinta National Forest32,698
418037Uinta National Forest9,694
Mt. Logan SouthWasatch-Cache National Forest17,014
WellsvilleWasatch-Cache National Forest1,717
Virginia (1)
AreaForestAcres
Oak KnobGeorge Washington National Forest10,882
Washington (3)
AreaForestAcres
Abercrombie - HooknoseColville National Forest33,862
Mt. BonaparteOkanogan National Forest10,891
TaneumWenatchee National Forest26,140
West Virginia (2)
AreaForestAcres
Mcgowan MountainMonongahela National Forest10,504
Middle MountainMonongahela National Forest19,020
Wyoming (5)
AreaForestAcres
Beartooth Proposed WildernessShoshone National Forest16,837
Gros Ventre MountainsBridger-Teton National Forest106,418
Libby FlatsMedicine Bow-Routt National Forest11,107
ReefShoshone National Forest16,817
Snowy RangeMedicine Bow-Routt National Forest29,660
References (33)
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  4. Biesboer, D. D. 1984. Nitrogen fixation associated with natural and cultivated stands of Typha latifolia L. (Typhaceae). Amer. J. Bot. 71(4):505-511.
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  6. Fassett, N. C. and B. Calhoun. 1952. Introgression between Typha latifolia and T. angustifolia. Evolution 6:267-379.
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  22. Roberts, E. H. 1972. Dormancy: a factor affecting seed survival in the soil. Viability of Seeds, Syracuse University Press, Syracuse, New York, pp. 321-359.
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