Typha angustifolia

Typha angustifolia may be difficult to separate from the tall cattail (Typha domingensis). Typha 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.

T. angustifolia, narrow-leaved cattail , is distinguished from Typha latifolia, broad-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. T. 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.

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.

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).

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).