Overview
Comprehensive Description
Description
General: Grass Family (Poaceae). Deergrass is a perennial bunchgrass obtaining heights of 5 feet when in bloom. It is part of the largest genus of warm season grasses in North America. The bunchgrass is found in dense, large clumps, but can occur as a continuous cover, in areas that are subjected to light, frequent ground fires. The culms are slender, narrow spike-like panicles, 9 to 12 dm. in length and less than 1.2 cm. wide. The numerous, small spikelets each have one awnless floret, with a 3-nerved lemma. The ligules are firm and truncate, 2-3 mm long. The leaves are 1.5 to 6 mm wide. The seeds are small, requiring about 2.5 million to make one pound. The dense, basal foliage is tufted and these large tufts, up to six feet across, are a distinguishing feature of the grass, along with the whip-like flower stalks.
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Distribution
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SPECIMEN BASED RECORD. Published protolog data.
http://www.tropicos.org/Reference/9990002
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SPECIMEN BASED RECORD. Published protolog data.
http://www.tropicos.org/Reference/9990002
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SPECIMEN BASED RECORD. Published protolog data.
http://www.tropicos.org/Reference/9990002
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SPECIMEN BASED RECORD. Published protolog data.
http://www.tropicos.org/Reference/9990002
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Espejo Serna, A., A. R. López-Ferrari & J. Valdés-Reyna. 2000. Poaceae. Monocot. Mexic. Sinopsis Floríst. 10: 7–236 [and index].
http://www.tropicos.org/Reference/1015183
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Beetle, A. A. 1977. Noteworthy grasses from Mexico V. Phytologia 37(4): 317–407.
http://www.tropicos.org/Reference/2538
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Beetle, A. A. 1995. Gram. México 4: 1–342. Secretaria de Agricultura y Recursos Hidraulícos: COTECOCA, México.
http://www.tropicos.org/Reference/1019699
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Anonymous. 1986. List-Based Rec., Soil Conserv. Serv., U.S.D.A. Database of the U.S.D.A., Beltsville.
http://www.tropicos.org/Reference/1103
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Soreng, R. J., G. Davidse, P. M. Peterson, F. O. Zuloaga, E. J. Judziewicz, T. S. Filgueiras & O. Morrone. 2003 and onwards. On-line taxonomic novelties and updates, distributional additions and corrections, and editorial changes since the four published volumes of the Catalogue of New World Grasses (Poaceae) published in Contr. U.S. Natl. Herb. vols. 39, 41, 46, and 48. http://www.tropicos.org/Project/CNWG:. In R. J. Soreng, G. Davidse, P. M. Peterson, F. O. Zuloaga, T. S. Filgueiras, E. J. Judziewicz & O. Morrone Internet Cat. New World Grasses. Missouri Botanical Garden, St. Louis.
http://www.tropicos.org/Reference/1024044
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Herrera Arrieta, Y. & A. Cortés Ortiz. 2010. Listado florístico y aspectos ecológicos de la familia Poaceae para Chihuahua, Durango y Zacatecas, México. J. Bot. Res. Inst. Texas 4(2): 711–738.
http://www.tropicos.org/Reference/100002652
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Espejo Serna, A., A. R. López-Ferrari & J. Valdés-Reyna. 2000. Poaceae. Monocot. Mexic. Sinopsis Floríst. 10: 7–236 [and index].
http://www.tropicos.org/Reference/1015183
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Beetle, A. A. 1977. Noteworthy grasses from Mexico V. Phytologia 37(4): 317–407.
http://www.tropicos.org/Reference/2538
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Gould, F. W. & R. Moran. 1981. The grasses of Baja California, Mexico. Mem. San Diego Soc. Nat. Hist. 12: 1–140.
http://www.tropicos.org/Reference/11232
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Peterson, P. M., J. Valdés-Reyna & Y. Herrera Arrieta. 2007. Muhlenbergiinae (Poaceae: Chloridoideae: Cynodonteae): from northeastern México. J. Bot. Res. Inst. Texas 1(2): 933–1000.
http://www.tropicos.org/Reference/1031940
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McVaugh, R. 1983. Gramineae. 14: 1–436. In R. McVaugh Fl. Novo-Galiciana. The University of Michigan, Ann Arbor.
http://www.tropicos.org/Reference/9853
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Beetle, A. A. 1995. Gram. México 4: 1–342. Secretaria de Agricultura y Recursos Hidraulícos: COTECOCA, México.
http://www.tropicos.org/Reference/1019699
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Correll, D. S. & M. C. Johnston. 1970. Man. Vasc. Pl. Texas i–xv, 1–1881. The University of Texas at Dallas, Richardson.
http://www.tropicos.org/Reference/1493
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Munz, P. A. & D. D. Keck. 1959. Cal. Fl. 1–1681. University of California Press, Berkeley.
http://www.tropicos.org/Reference/1717
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Munz, P. A. 1974. Fl. S. Calif. 1–1086. University of California Press, Berkeley.
http://www.tropicos.org/Reference/1719
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Barkworth, M. E., K. M. Capels, S. Long & M. B. Piep. 2003. Magnoliophyta: Commelinidae (in part): Poaceae, part 2. 25: i–xxv, 1–783. In Fl. N. Amer. Oxford University Press, New York.
http://www.tropicos.org/Reference/1021466
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Peterson, P. M. 2001. Muhlenbergia. In Catalogue of New World Grasses (Poaceae): II. Subfamily Chloridoideae. Contr. U.S. Natl. Herb. 41: 143–173.
http://www.tropicos.org/Reference/1003699
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Herrera Arrieta, Y. & P. M. Peterson. 2007. Muhlenbergia (Poaceae) de Chihuahua, México. Sida Bot. Misc. 29: i–x, 1–109.
http://www.tropicos.org/Reference/1030668
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National Distribution
United States
Origin: Unknown/Undetermined
Regularity: Regularly occurring
Currently: Unknown/Undetermined
Confidence: Confident
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Distribution
For current distribution, please consult the Plant Profile page for this species on the PLANTS Web site. It is found in sandy or gravely well-drained soils in scattered colonies in dry or damp places below 2150 m elevation from Shasta County in northern California south, extending into New Mexico, Texas, and Mexico.
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Physical Description
Morphology
Physical Description
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Type Information
Collection: Smithsonian Institution, National Museum of Natural History, Department of Botany
Verification Degree: Original publication and alleged type specimen examined
Preparation: Pressed specimen
Collector(s): C. H. T. Townsend & C. Barber
Year Collected: 1899
Locality: Sierra Madres near Colonia Garcia., Chihuahua, Mexico, North America
Elevation (m): 2134 to 2134
- Isotype: Piper, C. V. 1905. Proc. Biol. Soc. Wash. 18: 143.
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Collection: Smithsonian Institution, National Museum of Natural History, Department of Botany
Verification Degree: Original publication and alleged type specimen examined
Preparation: Pressed specimen
Collector(s): C. H. T. Townsend & C. Barber
Year Collected: 1899
Locality: In Sierra Madres, near Colonial Garcia, Chihuahua, Mexico, North America
Elevation (m): 2134 to 2134
- Holotype: Piper, C. V. 1905. Proc. Biol. Soc. Wash. 18: 143.
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Ecology
Dispersal
Establishment
Adaptation: Deergrass can withstand periodic flooding, but it cannot tolerate poorly-drained soils. The major plant communities it inhabits include valley grassland, streamsides, and meadow habitat. Additionally, deergrass is shade-intolerant and also occurs in grassland openings within chaparral, mixed conifer forests, and oak woodland plant communities, maintained with human-set or lightning fires. On most soil types, these grassland areas quickly revert to the surrounding dominant vegetation type without human or natural disturbance.
Broadcast Seeding: In California and the Southwest, deergrass can be broadcast seeded in the late spring or summer during the months of May, June, July, and August, with irrigation. The seeds are tiny and should be broadcast on top of the ground, and then run over with a ring roller or a culti-packer to compress the seeds slightly below the soil surface. For best results, sow at least four pounds of PLS (pure live seed) per acre, which amounts to 50 seeds per square foot. Deergrass is slow growing and germination rates can vary from two weeks up to two months. Fertilization of deergrass is not recommended, as it usually gives the alien weeds a competitive edge. Site preparation is extremely important for good establishment of deergrass. Both repetitive tillage and burning are recommended to drastically curtail weed competition. Repetitive tillage involves loosening the soil, irrigating, and cultivating the area with a disc harrow, following with a ring roller to kill the flush of annual weeds. This is done several times prior to seeding to exhaust the weed seed bank. Burning involves firing all residual dry matter prior to seeding.
Container Planting: Container planting is a more effective and less time consuming way of establishing deergrass, but it is more costly than seeding on a large scale. Deergrass seed can be sown into flats or, D-pots, stubby cells, or reforestation tubes in May. Plants can be planted out from containers in the fall of the same year in soil that has been moistened with the first rains, using standard planting procedures. Plants can also be sown in the fall in flats or containers and planted out the next summer or fall in the designated area. Plants should be spaced at a minimum width of 24 inches. Irrigating is not necessary if it is a normal rainfall year. Site preparation is the same as for a broadcast seeding. Larger bunchgrasses can also be divided in winter or early spring and transplanted. A good stand of deergrass can be established by container planting in one and one half years. It is thought that container planting with grown plugs is more effective than a seeding.
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Conservation
Conservation Status
National NatureServe Conservation Status
United States
Rounded National Status Rank: NNR - Unranked
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Status
Please consult the PLANTS Web site and your State Department of Natural Resources for this plant’s current status, such as, state noxious status and wetland indicator values.
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Management
Cultivars, improved and selected materials (and area of origin)
If possible, gather the seed from local sources, to maintain genetic diversity of deergrass. The flower stalks can be cut, bundled, and then beat over a tarp or bucket to release the seeds. The seeds are usually highly viable, and do not need special treatment. This grass is available from nurseries handling native plants.
Contact your local Natural Resources Conservation Service (formerly Soil Conservation Service) office for more information. Look in the phone book under ”United States Government.” The Natural Resources Conservation Service will be listed under the subheading “Department of Agriculture.”
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Management
Once established, deergrass is quite drought-tolerant. To maintain its vigor and reduce accumulated dead material, deergrass can be mowed or burned every several years. Burning or mowing should be in the fall, after it has gone to seed. Many tribes historically and probably prehistorically enhanced deergrass populations through firing deergrass stands in the fall in California every two to five years. Indian-set fires increased flower stalk yields, recycled nutrients, cleared away detritus, and promoted seedling production in the midst of reduced competition from other plants. According to Native American elders, these fires maintained the bunchgrass in greater numbers than would have occurred under natural conditions. Knowledge of past indigenous fire management of deergrass has important implications for mountain meadow habitat management for wildlife and maintenance of grassland openings within shrublands, woodlands, and forests for preservation of indigenous cultural traditions. Some areas could be managed with the dual objectives of indigenous harvesting of flower stalks and grazing after culm harvest. There are several fungi that infect the leaves of deergrass, causing debilitation, but usually not death. A fire would eliminate these pathogens.
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Relevance to Humans and Ecosystems
Benefits
Uses
Ethnobotanic: Deergrass is a significant basketry material to central and southern California Native Americans who utilize the flower stalks in the foundations of coiled baskets. Frequently thousands of flower stalks are needed for completion of each basket. Culms are gathered in late spring while still green, or summer or early fall when golden brown depending upon the tribe, individual family preference and elevation of the deergrass site.
Wildlife: In California, dense patches of deergrass provide cover during the fawning period of mule deer (Odocoileus hemionus) in mountain meadows and grassland openings. The younger palatable tufts are grazed by deer, horses, and cattle and can remain palatable if continually grazed. It is particularly sought for forage by animals when first resprouting after a burn. Older tufts are poor feed for livestock. The seeds provide food for songbirds and probably other birds as well. In sunny openings where deergrass occurs, it forms a larval food plant for one of the Satyrid butterflies, the California ringlet (Coenonympha california) and for the umber skipper (Poanes melane). Massive numbers of ladybugs overwinter in deergrass clumps.
Conservation: Deergrass is a valuable streambank stabilizer, as it has an extensive root system, and if grown in dense enough colonies, it can be an effective weed suppresser. In California, Pacific Gas and Electric is experimenting with growing dense colonies under powerline corridors. It's long, slender culms, and tall tufts making it an attractive plant for the garden.
Other Uses: Uses of deergrass include streambank stabilization, landscaping, forage, insectary, weed suppressant, and wildlife.
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Wikipedia
Muhlenbergia rigens
Muhlenbergia rigens, commonly known as Deergrass, is a warm season perennial bunchgrass found in sandy or well drained soils below 7,000 feet (2,100 m) in elevation in the Southwestern United States and parts of Mexico.
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Description
The plant Muhlenbergia rigens is characterized by dense, tufted basal foliage consisting of narrow pointed leaves that reach lengths of about 3 feet (0.91 m) and range in color from light silver-green to purple. The spikelike stems are less than half an inch wide and 3–4 feet (0.91–1.2 m) in length. During bloom, the numerous flowered panicles often reach heights of five feet and terminate in a single awnless floret with a 3-nerved lemma. Deergrass is characteristic of tallgrass prairie of much of the Western United States.
Distribution
The native range of the grass extends north into Shasta County, California, and south into New Mexico, Texas and Mexico. There it inhabits a wide range of ecotypes including grassland, riparian, chaparral, mixed conifer, and oak woodland communities. Deergrass can grow in areas with periodic flooding, but cannot tolerate standing water and poorly drained soils. It prefers full sun but is shade-tolerant.[1]
Uses
The young shoots are browsed by a variety of animals, [2] but with age the plant becomes unpalatable and is useful in an exposed garden setting for its deer resistance.[3] It has also been used for erosion prevention and streambank stabilization because of extensive root systems. Restoration efforts currently use deergrass to displace exotic invasive annuals that dominate current grassland ecosystems as well as remediate overtilled and eroded agricultural land where they anchor loose soils and return lost organic matter. Phytoremediative studies have also been conducted to test deergrass’s ability to remove chemicals from agricultural runoff. Deergrass’s dense stands and extensive roots act as a biofilter effective for herbicide, pesticide and particulate removal and breakdown.
Cultivation and habitat restoration
Muhlenbergia rigens, Deergrass, can be established in late spring and early summer by broadcast seeding with irrigation. For best results, 50 seeds per square foot are planted then lightly incorporated just below the soil surface with a culti-packer. Establishment is most successful when steps are taken to mitigate weed growth. Burning, discing and reduced fertilization schemes to reduce the weed seed bank are recommended.
Container planting is a highly effective way of establishing Deergrass. The seed can be sown in flats in May and transplanted in the fall of the same year. In California, except in areas of heavy frost, Muhlenbegia rigens can be successfully planted out in winter and spring to take advantage of seasonal rainfall.[4] Stand preparation should be the same as when broadcast-seeded. During transplant, plants should be spaced with a minimum of two feet between them. After establishment little management is required. Irrigation is unnecessary in normal rainfall years and fertilization is not recommended as it may increase weed competition. Burning or mowing can be used every few years to reduce accumulated dead matter.
Because Muhlenbergia rigens uses C4 carbon fixation, it gains an advantage in conditions of drought and high temperature. This characteristic, along with its attractiveness, has gained the plant recent attention as an ornamental in xeriscapes in yards and parks. Studies have also demonstrated a high tolerance to salt suggesting possible irrigation using low quality reclaimed waste-water sources at very low cost.[5]
Wildlife
Muhlenbergia rigens is a cover for mule deer during fawning periods and studies have equated reduced deer populations with overgrazed deergrass stands in and near cattle pasture.[6] Young shoots and leaves are grazed by deer, horses and cattle. The tall grass is an overwintering host for many species of Lepidoptera and ladybug, which along with deergrass seed, provides food for many different bird species.
History
Deergrass was important to many Native American tribes who used its long seedstalks as the principal material in coiled baskets. Deergrass underwent an early form of cultivation by many California tribes who regularly burned areas to maintain stands of deergrass, and induce the production of long straight stalks for use in basketry. Each basket required over 3000 stalks, driving the need for cultivation[7] It is believed that much of deergrass’s current distribution is due to propagation by Native Americans.
References
- ^ http://www.smgrowers.com/products/plants/plantdisplay.asp?plant_id=729
- ^ http://ucanr.org/sites/scmg/Plant_of_the_Month/Muhlenbergia_Rigens/
- ^ http://www.yerbabuenanursery.com/viewplant.php?pid=13
- ^ http://www.laspilitas.com/advanced/advwhentoplant.htm
- ^ Hunter, KAM, Wu, L. (2005). Morphological and Physiological Response of Five Californian Native Grass Species to Moderate Salt Spray: Implications for Landscape Irrigation with Reclaimed Water. Journal of Plant Nutrition. 28 247-270
- ^ Bowyer, RT. Bleich, VC. (1984). Effects of cattle grazing on selected habitats of southern mule deer. California Fish and Game. 70:4 240-247
- ^ Jordan, TA. (2003). Ecological and Cultural Contributions of Controlled Fire Use by Native Californians: A Survey of Literature. American Indian Culture and Research Journal. 27:1 77-90.
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