Difference between revisions of "Sorghastrum nutans"
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===Fire ecology=== <!--Fire tolerance, fire dependence, adaptive fire responses--> | ===Fire ecology=== <!--Fire tolerance, fire dependence, adaptive fire responses--> | ||
| − | Frequencies in a non-burned Florida site (NB66) had frequencies of 45 in 1966 and 75 in 2013, suggesting ''S. nutans'' does better without burning.<ref name="Clewell 2014">Clewell AF (2014) Forest development 44 years after fire exclusion in formerly annually burned oldfield pine woodland, Florida. Castanea 79(3):147-167.</ref> However, another study in Kansas showed coverage of unburned areas at 6.3%, while those burned at 4 year intervals and annually had coverage of 16.5 and 42.2%, respectively.<ref name="Abrams 1988">Abrams MD (1988) Effects of burning regime on buried seed banks and canopy coverage in a Kansas tallgrass prairie. The Southwestern Naturalist 33(1):65-70.</ref> | + | Frequencies in a non-burned Florida site (NB66) had frequencies of 45 in 1966 and 75 in 2013, suggesting ''S. nutans'' does better without burning.<ref name="Clewell 2014">Clewell AF (2014) Forest development 44 years after fire exclusion in formerly annually burned oldfield pine woodland, Florida. Castanea 79(3):147-167.</ref> However, another study in Kansas showed coverage of unburned areas at 6.3%, while those burned at 4 year intervals and annually had coverage of 16.5 and 42.2%, respectively.<ref name="Abrams 1988">Abrams MD (1988) Effects of burning regime on buried seed banks and canopy coverage in a Kansas tallgrass prairie. The Southwestern Naturalist 33(1):65-70.</ref> Still other studies in an Illinois and Wisconsin prairies did not see any affect on the reproductive tillering, cover, or incidence of ''S. nutans''.<ref name="Copeland et al 2002">Copeland TE, Sluis W, Howe HF (2002) Fire season dominance in an Illinois tallgrass prairie restoration. Restoration Ecology 10(2)315-323.</ref><ref name="Howe 1994">Howe HF (1994) Response of early- |
| + | and late-flowering plants to fire season in experimental prairies. Ecological Applications 4(1):121-133.</ref> | ||
===Pollination=== | ===Pollination=== | ||
Revision as of 15:26, 17 January 2018
| Sorghastrum nutans | |
|---|---|
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| Photo by John Hilty hosted at IllinoisWildflowers.info | |
| Scientific classification | |
| Kingdom: | Plantae |
| Division: | Magnoliophyta - Flowering plants |
| Class: | Liliopsida - Moncots |
| Order: | Poales |
| Family: | Poaceae |
| Genus: | Sorghastrum |
| Species: | S. nutans |
| Binomial name | |
| Sorghastrum nutans (L.) Nash | |
| |
| Natural range of Sorghastrum nutans from USDA NRCS Plants Database. | |
Common Name(s): yellow indiangrass;[1] indiangrass[2]
Contents
Taxonomic Notes
Synonym(s): S. avenaceum;[1][2] Andropogon nutans[2]
Description
Sorghastrum nutans is a monoecious perennial graminoid.[2] It is a bunching sod-forming grass with broad blue-green blades and soft plume-like golden-brown seed heads. This species can reach heights of 3-8 ft (0.91-2.44 m).[3] Its shoot forms a single terminal inflorescence. Dried seeds are between 0.07-1.25 mg, averaging 0.47 mg.[4]
Distribution
This species can be found in 42 of the 48 lower United States, from Arizona, northward through Utah, Wyoming, and Montana, and all states eastward. It also occurs in parts of Quebec, Ontario, Manitoba, and Saskatchewan provinces of Canada and in Mexico.[1][2]
Ecology
Habitat
It is one of the dominant grasses of tall-grass prairies but can be found in xeric and mesic woodlands and forests, along powerline right-of-ways and roadbanks, and in open habitats and forested landscapes.[1] In clayhill longleaf woodlands, S. nutans occurred in 71% of plots with a mean cover of 2.01 m2.[5]
Phenology
Flowering occurs from late August through October.[1] A report of flowering in November also exists.[6]
Seed dispersal
S. nutans primarily propagates via vegetative propagation and yields few viable seeds during drought years (as cited in [7]).
Fire ecology
Frequencies in a non-burned Florida site (NB66) had frequencies of 45 in 1966 and 75 in 2013, suggesting S. nutans does better without burning.[8] However, another study in Kansas showed coverage of unburned areas at 6.3%, while those burned at 4 year intervals and annually had coverage of 16.5 and 42.2%, respectively.[7] Still other studies in an Illinois and Wisconsin prairies did not see any affect on the reproductive tillering, cover, or incidence of S. nutans.[9][10]
Pollination
Individuals of S. nutans are wind pollinated.[4]Each inflorescence typically releases pollen from 0600 to 1000 for 8 days.[11]
Use by animals
This species provides nesting material and structure for native bees to build their nests. Caterpillars, including those of the pepper and salt skipper (Amblyscirtes hegon) use it for food.[3]
Conservation and Management
Cultivation and restoration
Seeds collected in the fall can be propagated by sowing unstratified seeds in the fall or stratified seeds in the spring. Seeds require dry stratification.[3]
Photo Gallery
References and notes
- ↑ 1.0 1.1 1.2 1.3 1.4 Weakley AS (2015) Flora of the Southern and Mid-Atlantic States. Chapel Hill, NC: University of North Carolina Herbarium.
- ↑ 2.0 2.1 2.2 2.3 2.4 USDA NRCS (2016) The PLANTS Database (http://plants.usda.gov, 17 January 2018). National Plant Data Team, Greensboro, NC 27401-4901 USA.
- ↑ 3.0 3.1 3.2 Plant database: Sorghastrum nutans. (17 January 2018) Lady Bird Johnson Wildflower Center. URL: https://www.wildflower.org/plants/result.php?id_plant=SONU2
- ↑ 4.0 4.1 McKone MJ, Lund CP, O'Brien JM (1998) Reproductive biology of two dominant prairie grasses (Andropogon gerardii and Sorghastrum nutans, Poaceae): Male-biased sex allocation in wind-pollinated plants? American Journal of Botany 85(6):776-783.
- ↑ Carr SC, Robertson KM, Peet RK (2010) A vegetation classification of fire-dependent pinelands of Florida. Castanea 75(2)153-189.
- ↑ Nelson G (17 January 2018) PanFlora. Retrieved from gilnelson.com/PanFlora/
- ↑ 7.0 7.1 Abrams MD (1988) Effects of burning regime on buried seed banks and canopy coverage in a Kansas tallgrass prairie. The Southwestern Naturalist 33(1):65-70.
- ↑ Clewell AF (2014) Forest development 44 years after fire exclusion in formerly annually burned oldfield pine woodland, Florida. Castanea 79(3):147-167.
- ↑ Copeland TE, Sluis W, Howe HF (2002) Fire season dominance in an Illinois tallgrass prairie restoration. Restoration Ecology 10(2)315-323.
- ↑ Howe HF (1994) Response of early- and late-flowering plants to fire season in experimental prairies. Ecological Applications 4(1):121-133.
- ↑ Jones MD, Newell LC (1946) Pollination cycles and pollen dispersal in relation to grass improvement. University of Nebraska College of Agriculture, Agricultural Experiment Station, Research Bulletin 148.
