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INTRODUCTORY
ABBREVIATION:NASVIR
SYNONYMS:Stipa viridula Trin [52,55,64,77,105,141]
NRCS PLANT CODE [135]:NAVI4
COMMON NAMES:green needlegrass feather bunchgrass green stipagrass
TAXONOMY:The currently accepted scientific name of green needlegrass is Nassella viridula (Trin.) Barkworth (Poaceae) [76]. Green needlegrass occasionally hybridizes with Indian ricegrass (Achnatherum hymenoides) to produce Achnella caduca (Beal) Barkworth, a sterile plant [52,71].
LIFE FORM:Graminoid
FEDERAL LEGAL STATUS:No special status
OTHER STATUS:In Idaho, the Natural Heritage Program and Conservation Data Center list green needlegrass as "imperiled because of rarity or because other factors demonstrably make it very vulnerable to extinction (typically 6 to 20 occurrences)." The Native Plant society lists green needlegrass as a type 2: "taxa likely to be classified as priority 1 within the foreseeable future in Idaho, if factors contributing to their population decline or habitat degradation or loss continue." The Bureau of Land Management in Idaho lists green needlegrass as sensitive: "taxa (1) that are under status review by U. S. Fish and Wildlife Service/National Marine Fisheries Service, (2) whose numbers are declining so rapidly that federal listing might become necessary, (3) with typically small and widely dispersed populations, or (4) inhabiting ecological refugia or other specialized unique habitats." It is secure globally [70].
AUTHORSHIP AND CITATION:Taylor, Jennifer L. (2001, March). Nassella viridula. In: Remainder of Citation DISTRIBUTION AND OCCURRENCE
GENERAL DISTRIBUTION:Green needlegrass occurs from Canada southward through Montana, mainly east of the Continental Divide, to Arizona and New Mexico [44,52]. It is native to the Great Plains north of Kansas and to Wisconsin and Illinois in the east [43]. Green needlegrass has been introduced in many parts of eastern North America [52,77]. In Wisconsin and Illinois, green needlegrass has been found along railroad rights-of-way [39,97].
ECOSYSTEMS [45]:FRES20 Douglas-fir FRES21 Ponderosa pine FRES29 Sagebrush FRES30 Desert shrub FRES35 Pinyon-juniper FRES36 Mountain grasslands FRES38 Plains grasslands FRES39 Prairie FRES40 Desert grasslands
STATES:
BLM PHYSIOGRAPHIC REGIONS [6]:6 Upper Basin and Range 7 Lower Basin and Range 8 Northern Rocky Mountains 9 Middle Rocky Mountains 10 Wyoming Basin 11 Southern Rocky Mountains 12 Colorado Plateau 13 Rocky Mountain Piedmont 14 Great Plains 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands
KUCHLER PLANT ASSOCIATIONS [86]:K011 Western ponderosa forest K012 Douglas-fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K019 Arizona pine forest K022 Great Basin pine forest K038 Great Basin sagebrush K050 Fescue-wheatgrass K051 Wheatgrass-bluegrass K055 Sagebrush steppe K056 Wheatgrass-needlegrass shrubsteppe K063 Foothills prairie K064 Grama-needlegrass-wheatgrass K065 Grama-buffalo grass K066 Wheatgrass-needlegrass K067 Wheatgrass-bluestem-needlegrass K068 Wheatgrass-grama-buffalo grass K069 Bluestem-grama prairie K070 Sandsage-bluestem prairie K074 Bluestem prairie K075 Nebraska Sandhills prairie
SAF COVER TYPES [37]:210 Interior Douglas-fir 219 Limber pine 220 Rocky Mountain juniper 237 Interior ponderosa pine 239 Pinyon-juniper
SRM (RANGELAND) COVER TYPES [119]:101 Bluebunch wheatgrass 102 Idaho fescue 104 Antelope bitterbrush-bluebunch wheatgrass 105 Antelope bitterbrush-Idaho fescue 107 Western juniper/big sagebrush/bluebunch wheatgrass 210 Bitterbrush 301 Bluebunch wheatgrass-blue grama 302 Bluebunch wheatgrass-Sandberg bluegrass 303 Bluebunch wheatgrass-western wheatgrass 304 Idaho fescue-bluebunch wheatgrass 306 Idaho fescue-slender wheatgrass 307 Idaho fescue-threadleaf sedge 309 Idaho fescue-western wheatgrass 310 Needle-and-thread-blue grama 311 Rough fescue-bluebunch wheatgrass 312 Rough fescue-Idaho fescue 314 Big sagebrush-bluebunch wheatgrass 315 Big sagebrush-Idaho fescue 316 Big sagebrush-rough fescue 317 Bitterbrush-bluebunch wheatgrass 318 Bitterbrush-Idaho fescue 323 Shrubby cinquefoil-rough fescue 401 Basin big sagebrush 402 Mountain big sagebrush 403 Wyoming big sagebrush 408 Other sagebrush types 504 Juniper-pinyon pine woodlands 601 Bluestem prairie 602 Bluestem-prairie sandreed 603 Prairie sandreed-needlegrass 604 Bluestem-grama prairie 606 Wheatgrass-bluestem-needlegrass 607 Wheatgrass-needlegrass 608 Wheatgrass-grama-needlegrass 609 Wheatgrass-grama 610 Wheatgrass 611 Blue grama-buffalo grass 612 Sagebrush-grass 613 Fescue grassland 614 Crested wheatgrass 615 Wheatgrass-saltgrass-grama 703 Black grama-sideoats grama 704 Blue grama-western wheatgrass 706 Blue grama-sideoats grama 707 Blue grama-sideoats grama-black grama 708 Bluestem-dropseed 709 Bluestem-grama
HABITAT TYPES AND PLANT COMMUNITIES:Published classifications listing green needlegrass as an indicator species or a dominant component of community types or plant associations are listed below:
Conditions and trends on ponderosa pine ranges in Colorado [23] North and South Dakota: Montana: In Wyoming and Utah, green needlegrass is found with Wyoming big sagebrush, mountain big sagebrush (Artemisia tridentata ssp. vaseyana), basin big sagebrush (A. t. ssp. tridentata), antelope bitterbrush [57,78], shrubby cinquefoil, and common juniper (Juniperus communis) [106]. It is a codominant of western wheatgrass and spike fescue (Leucopoa kingii) [15]. Green needlegrass is also associated with Sandberg bluegrass [57], needle-and-thread grass, cheatgrass, Indian ricegrass [78], and sedges [57]. In Colorado and Nebraska, green needlegrass is found in the understory of interior ponderosa pine with blue grama, cheatgrass, Kentucky bluegrass, needle-and-thread grass, western wheatgrass, little bluestem, sideoats grama, prairie sandreed, plains muhly, prairie Junegrass, Japanese brome, threadleaf sedge, sun sedge, dandelions (Taraxacum spp.), common juniper, wax currant (Ribes cereum), fringed sage, and common snowberry (Symphoricarpos albus) [83,132]. In Alberta, green needlegrass occurs in the wheatgrass-bluegrass (Agropyron spp.-Poa spp.) community, reedgrass-wheatgrass (Calamagrostis spp.-Agropyron spp.) community [117], and rough fescue (Festuca altaica) association [74]. In Saskatchewan, Manitoba, and Alberta, green needlegrass is codominant with western wheatgrass, needle-and-thread grass, blue grama, and buffalo grass [5,10,84,92,104,151]. It is associated with Sandberg bluegrass, plains muhly, threadleaf sedge [5], prairie Junegrass [5,84,151], western wheatgrass [5,104] plains reedgrass, sun sedge, obtuse sedge (Carex obtusata) [84,151], timber oatgrass (Danthonia intermedia), Idaho fescue, porcupine grass [74,84,151], needleleaf sedge, [84,151], Pumpelly brome (Bromus pumpellianus), and pinegrass (Calamagrostis rubescens) [74]. Green needlegrass is associated with the shrubs fringed sagebrush [5,84,151], plains silver sagebrush, and Gardner's saltbush, winterfat (Krascheninnikovia lanata) [5]. It is also found with little clubmoss (Selaginella densa), prairie goldenrod (Solidago missouriensis), pussytoes, and plains prickly-pear [5]. VALUE AND USE
IMPORTANCE TO LIVESTOCK AND WILDLIFE:Green needlegrass is considered "good" forage based on palatability, nutritive content, and dependability as a forage supply [98,111,128]. The awns do not trouble livestock [98,128]. Green needlegrass is used for hay and pasture production [18,133] and can produce good quality hay on favorable sites [128]. The seeds of green needlegrass are eaten by small mammals and songbirds, such as Vesper sparrow [7,127,139]. It is eaten by elk [93,122], Kaibab mule deer [69], and cattle [93].
PALATABILITY:Green needlegrass is moderately to highly palatable to cattle all year, more palatable when green [18,42,50,127,139]. It is unpalatable to bison once it is ripe [104]. Energy and protein content have been rated as fair [31]. The palatability of green needlegrass for livestock and wildlife species is rated as follows [31]:
NUTRITIONAL VALUE:Green needlegrass is a highly nutritious forage plant [42,79]. The highest protein content is in the early leaf stage and crude fiber content increases as development progresses [61]. Johnston and Bezeau [74] rate the nutritive value of green needlegrass in Alberta, Canada:
The food value of green needlegrass for wildlife species is rated as follows [31]:
COVER VALUE:Blue-winged teal, green-winged teal, northern shovelers, and pintails frequently select green needlegrass for nest sites because of its height [34,130]. It also provides additional concealment of nest sites for Brewer's and Vesper sparrow [7]. Grosz [53] observed green needlegrass at sharp-tailed grouse brood sites. The value of green needlegrass as cover for domestic animals and wildlife is rated as follows [31]:
VALUE FOR REHABILITATION OF DISTURBED SITES:Green needlegrass is relatively easy to establish [34]. It has been used in cool-season seeding mixtures, because of its early spring growth; it stays green for a long time, tolerates cold well, and has good seedling vigor. A problem with seed dormancy has hindered its use (see Botanical Characteristics, Regeneration Processes) [128]. Green needlegrass has been used to seed rangelands, pastures, and hay and to stabilize erosive sandy to clayey soils in the northern Great Plains [129,139]. It has been planted on reclaimed strip-mined sites in North Dakota [21,28] and Montana, as a part of native species grass seed mixtures on strip-mined lands [24,28,38]. Green needlegrass "has good potential for revegetation of abused rangeland" [42]. If green needlegrass is successfully established, it may persist as a dominant species on revegetated mined lands [30].
OTHER USES AND VALUES:No entry
MANAGEMENT CONSIDERATIONS:Green needlegrass decreases with grazing and spring deferment will benefit the grass [50,68,89,91,110,128]. It is grasshopper resistant and has no major diseases, but can occasionally be leaf-rust infested [139]. The presence of green needlegrass "on the more moist north-facing grasslands" indicates grazing of light to moderate levels in South Dakota [27]. It is a dominant grass on most upland range sites in high or excellent range condition [36,48]. Green needlegrass requires dormant fall plating [66]. Sites and planting dates must be chosen with moisture and germination in mind [44]. BOTANICAL AND ECOLOGICAL CHARACTERISTICS
GENERAL BOTANICAL CHARACTERISTICS:Green needlegrass is a tufted, perennial, native, long-lived, cool-season bunchgrass [1,8,14,18,20,24,29,30,36,43,48,66,75,95,100,102,126,128]. At maturity, the plants are 12 to 48 inches (30-122 cm) tall [4,26,50,52,62,73,87,98,109,127,128,139,141]. It has "good" drought tolerance [34,44,109,127], is moderately tolerant of flooding [58] and short-term submergence [139], and is capable of vigorous seedling growth [79]. Green needlegrass has a weak tolerance to shade from scattered shrubs and woodland openings and is very winter hardy [139]. The numerous, mostly basal leaves, are flat to involute and taper to threadlike tips [139]. Average length of leaves ranges from 4 to 12 inches (10.2-30.5 cm) [127]. Inflorescences are narrow, loose spikelets and 4 to 8 inches (10-20 cm) [62,98] long. Awns are bent twice and are 0.75 to 1.5 inches (1.9-3.8 cm) long [52,62,73,98,141]. Old sheath bases are often persistent [141]. Green needlegrass has a deep, up to 4 to 5 feet (122-152 cm) [140], fibrous root system [4,22,89,127,139], similar to needle-and-thread grass. The main roots are 0.04 inch (1 mm) in diameter; lateral spread is 14 inches (35.6 cm) in the first 6 inches (15.2 cm) of soil, and 18 inches (45.7 cm) in the first 12 inches (30.5 cm). The system is well branched and rootlets are abundant to depths of 2.5 feet (76.2 cm) [140].
RAUNKIAER LIFE FORM [108]:Hemicryptophyte
REGENERATION PROCESSES:Green needlegrass reproduces from seed and through tillering [95,98]. New seeds of green needlegrass have a higher occurrence of dormancy and a lower germination rate than mature seeds. Stratification in moist sand was found to be the best treatment to break dormancy. Fall plantings are successful because overwintering in soil can break the dormancy [113].
SITE CHARACTERISTICS:Green needlegrass is found on foothills, open hillsides and parks, in mountain meadows, canyons, and open woodlands [52,58,62]. It is a pioneer on abandoned croplands and coarse textured disturbed sites [139]. Green needlegrass is generally found in semi-arid, continental climates in a wide range of elevations [7,33,48]. Elevational ranges for green needlegrass are as follows:
Green needlegrass is found in a wide range of temperatures. Mean annual temperatures where green needlegrass is present are 3.4 to 117 degrees Fahrenheit (-15.9 to 47 oC). Green needlegrass occurs in areas with an average precipitation of 10-26 inches (254-660 mm) and the majority of the precipitation occurs between April and September [5,9,11,20,124,134,148]. Mean annual precipitation ranges for green needlegrass are as follows:
Soils: Green needlegrass is found on a variety of soil types [4,9,32,36,48,49,51,83,84,88,103,109,110,123,144,151]. It is tolerant of heavy clay soils, is less common on loams and sandy soils [91,127], and is weakly to moderately tolerant of soil salinity [139].
SUCCESSIONAL STATUS:In North Dakota, green needlegrass is considered a major species of the climax vegetation with western wheatgrass, blue grama, needle-and-thread grass, and threadleaf sedge [59]. It is considered a major climax grass, dominant with western wheatgrass [101]. Green needlegrass is an early seral species on disturbed sites [95].
SEASONAL DEVELOPMENT:Green needlegrass is one of the first in its association to start spring growth in the western Northern Great Plains [58]. It generally starts growth in March, grows vegetatively in May and June, heads out in June, and matures in July [4,22,97,127,139]. Goetz [50] observed these dates of development in North Dakota during 1955-1962:
White and Wight [145] observed these dates of development in Montana during 1975 and 1976:
FIRE ECOLOGY
FIRE ECOLOGY OR ADAPTATIONS:Effect of fire on green needlegrass depends on season of burn and site characteristics [144]. Depending on the phenological state of the plant, green needlegrass increases or decreases following fire [80,144]. Aboveground vegetation of green needlegrass is usually consumed by fire, but individual culms may survive [36]. Regeneration is through seed and tillering [143]. The effects of fire, increases in growth or decreases in vigor, can be immediate and last up to 3 years following the fire [33,40,81,103,105,141] Fire regimes for plant communities and ecosystems in which green needlegrass occurs are summarized below. For further information regarding fire regimes and fire ecology of communities and ecosystems where green needlegrass if found, see the 'Fire Ecology and Adaptations' section of the FEIS species summary for the plant community or ecosystem dominants listed below.
**(mean)
POSTFIRE REGENERATION STRATEGY [125]:Tussock graminoid Initial off-site colonizer (off-site, initial community) FIRE EFFECTS
IMMEDIATE FIRE EFFECT ON PLANT:Green needlegrass is top-killed or killed by fire. The number of inflorescences, basal area, and leaf lengths can be decreased by fire [25,36]. Specific effects of fire depend on season of burn, fire intensity, and severity [144]. Whisenant [144] stated that green needlegrass is intolerant of spring burning.
DISCUSSION AND QUALIFICATION OF FIRE EFFECT:No entry
PLANT RESPONSE TO FIRE:Different researchers have observed various effects responses of green needlegrass to burning, depending on season of burning and site characteristics. Green needlegrass has been found to increase following spring burning [80]. Following an April prescribed burn in South Dakota, Forde [40] found a decrease in percent ground cover the year of the fire, but observed rapid increases 2 years following the fire. Whisenant [144] in South Dakota found burning caused a significant decrease in standing green needlegrass, approximately one-third of unburned plots, for at least 3 growing seasons following a fire in April. Schripema [116] found that green needlegrass was decreased by spring burning in South Dakota. Green needlegrass was absent from burned plots for 3 years postfire and was never found in flower following a September fire in North Dakota [33]. Olson [105] found canopy coverage of green needlegrass decreased in the 2nd postburn season following 2 annual burns in North Dakota. Kirsch [81] found green needlegrass to increase with burning in North Dakota. Nimir [103] observed a statistically insignificant decrease in green needlegrass on one burned site in Montana, but not the other.
DISCUSSION AND QUALIFICATION OF PLANT RESPONSE:No entry
FIRE MANAGEMENT CONSIDERATIONS:The effects of fire on green needlegrass vary with season of burn and site characteristics. Higgins [63] found the best response of green needlegrass to fire with March-April (very-early spring) or August-September (late summer) in Northern Mixed Prairie. FIRE CASE STUDY
CASE NAME:Ordway Memorial Prairie, South Dakota
REFERENCE:Engle, D. M.; Bultsma, P. M. 1984 [36]
FIRE CASE STUDY AUTHORSHIP:Tirmenstein, D. 1987.
SEASON/SEVERITY CLASSIFICATION:late spring, May 13-16, 1980 / not determined summer, June 16, 1980 / not determined
STUDY LOCATION:The burn occurred on the Samuel H. Ordway Memorial Prairie in north-central South Dakota, 6.2 miles (10 km) west of Leola.
PREFIRE VEGETATIVE COMMUNITY:Preburn vegetation comprised species occurring in the prairie pothole region of the northern mixed-grass prairie. Associated plants included western wheatgrass (Pascopyrum smithii), needle-and-thread grass (Hesperostipa comata), green needlegrass (Nassella viridula), big bluestem (Andropogon gerardii var. gerardii), and Kentucky bluegrass (Poa pratensis).
TARGET SPECIES PHENOLOGICAL STATE:
|
| Wind | Air temperature | Relative humidity | |
| May 13-16, 1980 | 3-13 km/h | 39.2 to 66.2 degrees Fahrenheit (4-19 oC) | 23-45% |
| June 16, 1980 | 0-24 km/h | 68 to 86 degrees Fahrenheit (20-30 oC) | 42-66% |
Spring growth was consumed by the fire and some plants were killed. Leaf length, number of inflorescences and basal area were decreased by burning. Individuals that survived the fire had as much or more growth than those on the unburned plot 1 year postfire. Measured fire effects were:
|
Measured August 8-11, 1980 |
May 13-16 | June 16 | control |
| leaf length (cm) | 24.7 | 23.3 | 41.1 |
| inflorescences/m2 | 2.8 | 0.0 | 16.8 |
| basal area (cm2) | 10.3 | 6.9 | 20.8 |
|
Measured August 8-11, 1981 |
May 13-16 | June 16 | control |
| leaf length (cm) | 38.9 | 37.3 | 57.5 |
| inflorescences/m2 | 32.9 | 34.0 | 19.7 |
| basal area (cm2) | 12.3 | 7.8 | 6.5 |
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