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SPECIES: Artemisia ludoviciana
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© Br. Alfred Brousseau, Saint Mary's College |
ECOSYSTEMS [42]:
FRES14 Oak-pine
FRES15 Oak-hickory
FRES17 Elm-ash-cottonwood
FRES20 Douglas-fir
FRES21 Ponderosa pine
FRES23 Fir-spruce
FRES28 Western hardwoods
FRES29 Sagebrush
FRES30 Desert shrub
FRES34 Chaparral-mountain shrub
FRES35 Pinyon-juniper
FRES36 Mountain grasslands
FRES37 Mountain meadows
FRES38 Plains grasslands
FRES39 Prairie
FRES40 Desert grasslands
FRES44 Alpine
STATES/PROVINCES: (key to state/province abbreviations)
UNITED STATES
AZ | AR | CA | CO | CT | DE | GA | ID | IL | IN |
IA | KS | KY | LA | ME | MD | MA | MI | MN | MS |
MO | MT | NE | NV | NH | NJ | NM | NY | NC | ND |
OH | OK | OR | PA | RI | SC | SD | TN | TX | UT |
VT | VA | WA | WI | WY | DC |
AB | BC | MB | NT | ON | PQ | SK |
B.C.N. | Chih. | Son. |
Sagebrush ecosystems: White sagebrush commonly occurs in sagebrush (Artemisia subsp.) communities. Shrub and tree associates include big sagebrush (A. tridentata), black sagebrush (A. nova), fringed sagebrush (A. frigida), shadscale saltbush (Atriplex confertifolia), curlleaf mountain-mahogany (Cercocarpus ledifolius), rubber rabbitbrush (Chrysothamnus nauseosus), green rabbitbrush (C. viscidiflorus), antelope bitterbrush (Purshia tridentata), Rocky mountain juniper (Juniperus scopulorum), western juniper (J. occidentalis), interior ponderosa pine (Pinus ponderosa var. scopulorum), Jeffrey pine (P. jeffreyi), and several oaks (Quercus spp.). Herbaceous understory associates include Indian ricegrass (Achnatherum hymenoides), blue grama (Bouteloua gracilis), buckwheat (Eriogonum spp.), ephedra (Ephedra spp.), Idaho fescue (Festuca idahoensis), rough fescue (Festuca altaica), needle-and-thread grass (Hesperostipa comata), prairie Junegrass (Koeleria macrantha), western wheatgrass (Pascopyrum smithii), Sandberg bluegrass (Poa secunda), plains bluegrass (P. arida), and bluebunch wheatgrass (Pseudoroegneria spicata) [37,72,115].
Chaparral-mountain shrub ecosystems: Common tree and shrub associates in these plant communities include alligator juniper (J. deppeana), oneseed juniper (J. monosperma), Utah juniper (J. osteosperma), Mexican pinyon (Pinus cembroides), Arizona white oak (Q. arizonica), canyon live oak (Q. chrysolepis), Emory oak (Q. emoryi), Gambel oak (Q. gambelii), silverleaf oak (Q. hypoleucoides), Mexican blue oak (Q. oblongifolia), shrub live oak (Q. turbinella), interior live oak (Q. wislizenii), chamise (Adenostoma fasciculatum), manzanita (Arctostaphylos spp.), ceanothus (Ceanothus spp.), bush chinquapin (Chrysolepsis sempervirens), curlleaf mountain-mahogany , birchleaf mountain-mahogany (C. betuloides), bigtooth maple (Acer grandidentatum), and bittercherry (Prunus emarginata). Understory associates include sideoats grama (B. curtipendula), hairy grama (B. hirsuta), and eastern Mojave buckwheat (Eriogonum fasciculatum) [37,72,115].
Plains grasslands: White sagebrush is particularly common in plains and prairie grassland communities. In plains grasslands, associates include Indian ricegrass, crested wheatgrass (Agropyron cristatum), desert wheatgrass (A. desertorum), big bluestem (Andropogon gerardii var. gerardii), sand bluestem (A. g. var. paucipilus), blue grama, sideoats grama, hairy grama, black grama (B. eriopoda), buffalo grass (Buchloe dactyloides), prairie sandreed (Calamovilfa longifolia), oatgrass (Danthonia spp.), Canada wildrye (Elymus canadensis), thickspike wheatgrass (E. lanceolatus), rough fescue, prairie Junegrass, needle-and-thread grass, porcupine grass (H. spartea), green needlegrass (Nassella viridula), tobosa (Pleuraphis mutica), Kentucky bluegrass (Poa pratensis), western wheatgrass, bluebunch wheatgrass, little bluestem (Schizachyrium scoparium), and alkali sacaton (Sporobolus airoides). Woody plants commonly occurring in these communities include fringed sagebrush, sand sagebrush (Artemisia filifolia), fourwing saltbush (Atriplex canescens), Ashe juniper (J. ashei), eastern redcedar (J. virginiana) winterfat (Krascheninnikovia lanata ), blackjack oak (Q. marilandica), post oak (Q. stellata), and live oak (Q. virginiana) [72,115].
Prairie grasslands: In prairie communities, common associates include threeawns (Aristida spp.), big bluestem, sand bluestem, blue grama, hairy grama, sideoats grama, buffalo grass, prairie sandreed, needle-and-thread grass, porcupine grass, prairie Junegrass, switchgrass (Panicum virgatum), little bluestem, indiangrass (Sorghastrum nutans), prairie dropseed (Sporobolus heterolepis), and giant dropseed (S. giganteus). Common woody associates are big sagebrush, black sagebrush, sand sagebrush, rubber rabbitbrush, green rabbitbrush, winterfat, saltbushes (Atriplex spp.), hickories (Carya spp.), eastern redcedar, eastern cottonwood (Populus deltoides), post oak, blackjack oak, and black oak (Q. velutina) [37,72,115].
White sagebrush usually occurs in scattered amounts and does not dominate extensive areas [118], though it may form dense stands locally in grassland communities [36]. White sagebrush may be dominant in Wyoming, commonly codominating forb communities with tobacco root (Valeriana edulis) [24,47]. This forb community is often found near subalpine fir (Abies lasiocarpa) habitat types. Other associates in the white sagebrush-tobacco root community type are Idaho fescue, Rocky Mountain goldenrod (Solidago multiradiata), thickstem aster (Eurybia integrifolia), sulphur-flower buckwheat (Eriogonum umbellatum), slender cinquefoil (Potentilla gracilis), elkweed (Frasera speciosa), and spike trisetum (Trisetum spicatum) [47]. In Alberta, white sagebrush may codominate with western wheatgrass. Other common associates in this community are riverbank sedge (Carex stenoptila), Kentucky bluegrass, curlycup gumweed (Grindelia squarrosa), and desert goosefoot (Chenopodium pratericola) [128]. White sagebrush is noted as a "differential species" in mixed-grass (Kentucky bluegrass dominant) and tallgrass (big bluestem dominant) prairie communities. In the mixed-grass community, other associates include western wheatgrass and smooth brome (Bromus inermis), while little bluestem is common in the tallgrass community [85].
Vegetation classifications identifying white sagebrush as a plant community dominant are listed below:
Alberta [128]White sagebrush is a native perennial forb or small shrub [103,119]. Stems seldom branch and are loosely clustered or solitary [59,119,131]. Though generally erect [119], alpine subspecies (e.g., A. l. subsp. incompta) may be decumbent compared to the more upright forms found at lower elevations [118]. White sagebrush grows 0.5 to 3 feet (0.15-1.0 m) tall [43,46,56,103,119,132] and has alternate, irregularly toothed leaves [119]. The inflorescence is a narrow, open to dense panicle reaching 2 to 12 inches (5-30 cm) in length. The many nodding flower heads are <7 mm in diameter [56,132]. Seeds are small achenes [123].
White sagebrush is often densely aggregated in pure stands 6.5 to 10 feet (2-3 m) in diameter, with all stalks connected by underground stems or rhizomes [36,56,59,69,96,103,119,131] that thicken with age. White sagebrush rhizomes and dense, coarse roots are generally found between 1 and 5.5 inches (2.5-14 cm) deep [96,118]. Root branching in the fibrous root system is so interlaced that a firm mesh forms in the upper 2 inches (5 cm) of soil [96,113]. White sagebrush roots may reach 27.5 inches (70 cm) deep [143].
Roots may be colonized by mycorrhizae [136]; when colonized, ramet growth rates and biomass are reduced, resulting in a reduction in size and density of white sagebrush [137]. Root nodulation is inconsistent [38,118,139], and it is difficult to confirm any significant degree of nitrogen fixation [118].
RAUNKIAER [104] LIFE FORM:Breeding system: White sagebrush is monoecious [118].
Pollination: White sagebrush is self- and wind pollinated [57,118].
Seed production: Most subspecies produce seed "adequately" [118]. The outer florets of white sagebrush are usually sterile, while the inner florets are usually fertile [119].
Seed dispersal: White sagebrush seeds are spread by wind, gravity, and water [123].
Seed banking: white sagebrush seed can last 4 to 6 years in warehouse storage [114]. As of this writing (2005), there is no information on viability of soil-stored seed.
Germination: No information is available on this topic. For information on artificial germination of white sagebrush, see Management Considerations.
Seedling establishment/growth: White sagebrush dies back at the end of the season, so annual production is equivalent to total aboveground mass at the end of the growing season [54,118].
Asexual regeneration: White sagebrush forms new aerial shoots from the bases of earlier shoots and from slender horizontal rhizomes [93,98]. Some subspecies reproduce aggressively by spreading rhizomes, while others express weaker rhizomes [118,123]. When strongly rhizomatous, white sagebrush can form colonies up to 50 feet (15 m) in diameter. A study in Montana found that on wet sites colonies advanced in all directions, but on dry sites colonies increased in diameter only in wet microsites (e.g. drainage depressions) [54].
SITE CHARACTERISTICS:White sagebrush is found on a wide range of soil types [118,119]. It is common on sandy to gravelly or stony sites, including scree slopes and rockslides [56,87,131,141]. White sagebrush is frequently found on exposed ridges and sites free of snow accumulation [118]. It is also found on silty soils, and may occur on soils with high lime content, though not abundantly [106].
The following table presents the elevational range of white sagebrush in the western United States:
California | 11,500 feet (<3500 m) | [56,87] |
Colorado | 3,500-10,000 ft (1,060-3,050 m) | [52] |
Nevada | 2,500-9,500 ft (760-2,900 m) | [64] |
New Mexico | 7,200-8,700 ft (2,200-2,600 m) | [50] |
Utah | 2,460-11,500 ft (750-3,500 m) | [132] |
Fire regimes: White sagebrush is found in a wide variety of habitat types and plant communities, so fire regimes also vary widely. No specific information regarding the interaction between white sagebrush and different fire regimes was found in the available literature. However, based on prescribed fire studies, frequent fire may substantially reduce white sagebrush on a site. For more information on the effects of frequent burning, see Fire Management Considerations.
The following list provides fire return intervals for plant communities and ecosystems where white sagebrush occurs. It may not be inclusive. Find further fire regime information for the plant communities in which this species may occur by entering the species name in the FEIS home page under "Find Fire Regimes".
Community or Ecosystem | Dominant Species | Fire Return Interval Range (years) |
bluestem prairie | Andropogon gerardii var. gerardii-Schizachyrium scoparium | < 10 [71,100] |
Nebraska sandhills prairie | A. g. var. paucipilus-Schizachyrium scoparium | < 10 [100] |
silver sagebrush steppe | Artemisia cana | 5-45 [55,102,138] |
sagebrush steppe | A. tridentata/Pseudoroegneria spicata | 20-70 [100] |
basin big sagebrush | A. t. var. tridentata | 12-43 [110] |
mountain big sagebrush | A. t. var. vaseyana | 15-40 [6,20,88] |
Wyoming big sagebrush | A. t. var. wyomingensis | 10-70 (40**) [126,142] |
saltbush-greasewood | Atriplex confertifolia-Sarcobatus vermiculatus | < 35 to < 100 |
desert grasslands | Bouteloua eriopoda and/or Pleuraphis mutica | 5-100 [100] |
plains grasslands | Bouteloua spp. | < 35 [100,138] |
blue grama-needle-and-thread grass-western wheatgrass | B. gracilis-Hesperostipa comata-Pascopyrum smithii | < 35 [100,107,138] |
blue grama-buffalo grass | B. g.-Buchloe dactyloides | < 35 [100,138] |
California montane chaparral | Ceanothus and/or Arctostaphylos spp. | 50-100 [100] |
curlleaf mountain-mahogany* | Cercocarpus ledifolius | 13-1,000 [8,111] |
mountain-mahogany-Gambel oak scrub | C. l.-Quercus gambelii | < 35 to < 100 |
blackbrush | Coleogyne ramosissima | < 35 to < 100 |
Arizona cypress | Cupressus arizonica | < 35 to 200 |
juniper-oak savanna | Juniperus ashei-Quercus virginiana | < 35 |
Ashe juniper | J. ashei | < 35 |
western juniper | J. occidentalis | 20-70 |
Rocky Mountain juniper | J. scopulorum | < 35 [100] |
cedar glades | J. virginiana | 3-22 [49,100] |
wheatgrass plains grasslands | Pascopyrum smithii | < 5-47+ [100,102,138] |
Engelmann spruce-subalpine fir | Picea engelmannii-Abies lasiocarpa | 35 to > 200 [5] |
pinyon-juniper | Pinus-Juniperus spp. | < 35 [100] |
Mexican pinyon | P. cembroides | 20-70 [91,120] |
Colorado pinyon | P. edulis | 10-400+ [40,45,66,100] |
Jeffrey pine | P. jeffreyi | 5-30 [5] |
interior ponderosa pine* | P. ponderosa var. scopulorum | 2-30 [5,10,75] |
Arizona pine | P. p. var. arizonica | 2-15 [10,27,112] |
eastern cottonwood | Populus deltoides | < 35 to 200 [100] |
quaking aspen (west of the Great Plains) | P. tremuloides | 7-120 [5,48,82] |
mountain grasslands | Pseudoroegneria spicata | 3-40 (10**) [4,5] |
Rocky Mountain Douglas-fir* | Pseudotsuga menziesii var. glauca | 25-100 [5,6,7] |
California mixed evergreen | P. m. var. menziesii-Lithocarpus densiflorus-Arbutus menziesii | < 35 |
California oakwoods | Quercus spp. | < 35 [5] |
oak-hickory | Quercus-Carya spp. | < 35 [129] |
oak-juniper woodland (Southwest) | Quercus-Juniperus spp. | < 35 to < 200 [100] |
northern pin oak | Q. ellipsoidalis | < 35 |
bear oak | Q. ilicifolia | < 35 [129] |
California black oak | Q. kelloggii | 5-30 [100] |
bur oak | Q. macrocarpa | < 10 |
oak savanna | Q. m./Andropogon gerardii-Schizachyrium scoparium | 2-14 [100,129] |
chestnut oak | Q. prinus | 3-8 |
post oak-blackjack oak | Q. stellata-Q. marilandica | < 10 |
black oak | Q. velutina | < 35 [129] |
interior live oak | Q. wislizenii | < 35 [5] |
little bluestem-grama prairie | Schizachyrium scoparium-Bouteloua spp. | < 35 [100] |
elm-ash-cottonwood | Ulmus-Fraxinus-Populus spp. | < 35 to 200 [35,129] |
Response of white sagebrush percent cover to fire is inconsistent. In a Kansas big bluestem-little bluestem-indiangrass prairie, white sagebrush percent cover decreased with burning during any season on upland sites and with spring burning on lowland sites after 8 years of burning during different seasons. On lowlands, percent cover increased with fall and winter burning [121]. In an Alberta rough fescue-porcupine grass grassland, canopy cover of white sagebrush increased in the 1st postburn growing season following both a spring and a fall burn [9]. Becker [13] also describes an increase in foliage after spring burning in a Minnesota big bluestem-prairie dropseed community. In an Arizona Santa Catalina Mountain Madrean oak community dominated by Emory oak, Mexican blue oak, and Arizona white oak, another study found a strong increase in white sagebrush cover following burning, with cover continuing to increase for 3 years after fire. The table below details changes in white sagebrush percent cover for 2 seasons following a June 1983 burn [21]:
Spring 1984 | Fall 1985 | |||
Aspect | Unburned | Burned | Unburned | Burned |
south | 4.12 | 1.89 | 2.89 | 6.82 |
east | 0.72 | 2.85 | 0.62 | 5.83 |
north | 0.67 | 1.96 | 1.07 | 7.63 |
A study of prescribed fire on green needlegrass-western wheatgrass plains grassland sites in North Dakota found no consistent postfire effect on white sagebrush cover [67].
The Research Project Summary Seasonal fires in Saskatchewan rough fescue prairie provides information on prescribed fire use and postfire response of plains grassland community species including white sagebrush.
FIRE MANAGEMENT CONSIDERATIONS:North slopes | South slopes | |||
Prefire (1970) | Postfire (1971) | Prefire (1970) | Postfire (1970) | |
lb/acre (kg/ha) | 50 (56) | 39 (44) | 111 (125) | 67 (75) |
% production | 4 | 2 | 9 | 4 |
Greater sage-grouse use white sagebrush for summer food and cover [105,130].
White sagebrush is an important food source for grasshoppers [70]. It is an almost exclusive host for the specialist grasshopper Hypochlora alba [17,18,69,76]. It is also the only known host of the fruit fly Eutreta simplex [44].
Palatability/nutritional value: White sagebrush palatability has been rated poor to fair for domestic cattle, sheep, and horses in Colorado, Montana, North Dakota, Utah, and Wyoming. Palatability domestic sheep is rated good in Utah [32].
A study by Bezeau and Johnston [15] found 5.8% average digestible protein in white sagebrush samples. The table below summarizes chemical analysis of white sagebrush from Arizona chaparral [125]:
Crude protein (%) | Ca (%) | P (%) |
9 | 0.64 | 0.32 |
Average chemical composition of white sagebrush in Alberta rough fescue grassland at 3 different stages of white sagebrush growth is summarized in the following table [61]:
Stage of growth | Protein (%) | Crude fat (%) | Crude fiber (%) | Ca (%) | P (%) | Carotene mg/kg) |
leaf | 15.40 | 2.85 | 25.20 | 0.90 | 0.23 | 42.75 |
heading | 10.55 | 5.10 | 26.80 | 0.90 | 0.17 | 37.40 |
seed-ripe | 8.87 | 4.30 | 29.17 | 0.97 | 0.16 | 25.30 |
Cover value: Cover value of white sagebrush has been rated poor to fair for big game animals, upland game birds, nongame birds, and waterfowl. It has been rated as good cover for small mammals in Utah, though rated poor elsewhere [32].
VALUE FOR REHABILITATION OF DISTURBED SITES:White sagebrush seeds germinate well in the laboratory at 59-77 oF (15-25 oC) [86]. Eddleman [36] found germination was highest at both 68 oF (20 oC) constant and 68/41 oF (20/5 oC) alternating temperatures, with germination improved by 3-month stratification. Other laboratory experiments conducted at 59 oF have found up to 95% germination in petri dishes, and 69% germination in soil tests. On filter paper, the following germination rates were achieved at different temperatures [54]:
Temperature | Germination (%) |
59 oF (15 oC) | 56 |
68 oF (20 oC) | 87 |
72 oF (22 oC) | 90 |
One laboratory analysis, however, found seed viability of white sagebrush was only 34.6% [23].
OTHER USES:Native American medicinal uses included treatment for sore throats, stomach ailments, and difficulty in childbirth [109,119]. White sagebrush leaves were also crushed and used as snuff to treat sinus attacks, nosebleeds, and headaches [53]. Tea made with white sagebrush was used in Mexican traditional medicine to alleviate intestinal pain [108]. An essential oil extracted from white sagebrush (A. l. subsp. mexicana) has been demonstrated to give symptomatic relief of diarrhea [144]. Extracts of white sagebrush have antifungal properties [80].
OTHER MANAGEMENT CONSIDERATIONS:1. Abrams, Marc D.; Hulbert, Lloyd C. 1987. Effect of topographic position and fire on species composition in tallgrass prairie in northeast Kansas. The American Midland Naturalist. 117(2): 442-445. [291]
2. Anderson, Kling L.; Smith, Ed F.; Owensby, Clenton E. 1970. Burning bluestem range. Journal of Range Management. 23: 81-92. [323]
3. Archibold, O. W.; Ripley, E. A.; Delanoy, L. 2003. Effects of season of burning on the microenvironment of fescue prairie in central Saskatchewan. Canadian Field Naturalist. 117(2): 257-266. [48371]
4. Arno, Stephen F. 1980. Forest fire history in the Northern Rockies. Journal of Forestry. 78(8): 460-465. [11990]
5. Arno, Stephen F. 2000. Fire in western forest ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 97-120. [36984]
6. Arno, Stephen F.; Gruell, George E. 1983. Fire history at the forest-grassland ecotone in southwestern Montana. Journal of Range Management. 36(3): 332-336. [342]
7. Arno, Stephen F.; Scott, Joe H.; Hartwell, Michael G. 1995. Age-class structure of old growth ponderosa pine/Douglas-fir stands and its relationship to fire history. Res. Pap. INT-RP-481. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 25 p. [25928]
8. Arno, Stephen F.; Wilson, Andrew E. 1986. Dating past fires in curlleaf mountain-mahogany communities. Journal of Range Management. 39(3): 241-243. [350]
9. Bailey, Arthur W.; Anderson, Murray L. 1978. Prescribed burning of a Festuca-Stipa grassland. Journal of Range Management. 31: 446-449. [373]
10. Baisan, Christopher H.; Swetnam, Thomas W. 1990. Fire history on a desert mountain range: Rincon Mountain Wilderness, Arizona, U.S.A. Canadian Journal of Forest Research. 20: 1559-1569. [14986]
11. Bayless, Steve. 1971. Relationships between big game and sagebrush. [Paper presented at the annual meeting of the Northwest Section of the Wildlife Society; 1971 March 25-26; Bozeman, MT]. 14 p. Unpublished paper on file with: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT. [17098]
12. Bean, Lowell John; Saubel, Katherine Siva. 1972. Telmalpakh: Chauilla Indian knowledge and usage of plants. Banning, CA: Malki Museum. 225 p. [35898]
13. Becker, Donald A. 1989. Five years of annual prairie burns. In: Bragg, Thomas A.; Stubbendieck, James, eds. Prairie pioneers: ecology, history and culture: Proceedings, 11th North American prairie conference; 1988 August 7-11; Lincoln, NE. Lincoln, NE: University of Nebraska: 163-168. [14037]
14. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434]
15. Bezeau, L. M.; Johnston, A. 1962. In vitro digestibility of range forage plants of the Festuca scabrella association. Canadian Journal of Plant Science. 42: 692-697. [441]
16. Biondini, M. E.; Steuter, A. A.; Grygiel, C. E. 1989. Seasonal fire effects on the diversity patterns, spatial distribution and community structure of forbs in the northern mixed prairie, USA. Vegetatio. 85: 21-31. [10180]
17. Blust, M. H.; Hopkins, T. L. 1987. Olfactory responses of a specialist and a generalist grasshopper to volatiles of Artemisia ludoviciana Nutt. (Asteraceae). Journal of Chemical Ecology. 13(8): 1893-1902. [46890]
18. Blust, Michael H.; Hopkins, Theodore L. 1987. Gustatory responses of a specialist and a generalist grasshopper to terpenoids of Artemisia ludoviciana. Entomologia Experimentalis et Applicata. 45(1): 37-46. [47304]
19. Brand, M. D.; Goetz, H. 1978. Secondary succession of a mixed grass community in southwestern North Dakota. Annual Proceedings of the North Dakota Academy of Science. 32(2): 67-78. [7512]
20. Burkhardt, Wayne J.; Tisdale, E. W. 1976. Causes of juniper invasion in southwestern Idaho. Ecology. 57: 472-484. [565]
21. Caprio, Anthony C.; Zwolinski, Malcolm J. 1995. Fire and vegetation in a Madrean oak woodland, Santa Catalina Mountains, southeastern Arizona. In: DeBano, Leonard F.; Ffolliott, Peter F.; Ortega-Rubio, Alfredo; [and others], technical coordinators. Biodiversity and management of the Madrean Archipelago: the sky islands of southwestern United States and northwestern Mexico: Proceedings; 1994 September 19-23; Tucson, AZ. Gen. Tech. Rep. RM-GRT-264. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 389-398. [26246]
22. Castetter, Edward F.; Opler, M. E. 1936. Ethnobiological studies in the American Southwest. III. The ethnobiology of the Chiricahua and Mescalero Apache. University of New Mexico Bulletin. 4(5): 1-63. [38173]
23. Clarke, Joseph W., DePuit, Edward J. 1981. Analysis of direct seeding methods for establishment of selected native shrub species on minesoils in southeastern Montana. In: Stelter, Lavern H.; DePuit, Edward J.; Mikol, Sharon A., tech. coords. Shrub establishment on disturbed arid and semi-arid lands: Proceedings of the symposium; 1980 December 2-3; Laramie, WY. Cheyenne, WY: Wyoming Game and Fish Department: 89-103. [43310]
24. Collins, Ellen I. 1984. Preliminary classification of Wyoming plant communities. Cheyenne, WY: Wyoming Natural Heritage Program/The Nature Conservancy. 42 p. [661]
25. Collins, Scott L. 1987. Interaction of disturbances in tallgrass prairie: a field experiment. Ecology. 68(5): 1243-1250. [2708]
26. Collins, Scott L.; Glenn, Susan M.; Gibson, David J. 1995. Experimental analysis of intermediate disturbance and initial floristic composition: decoupling cause and effect. Ecology. 76(2): 486-492. [25697]
27. Cooper, Charles F. 1961. Pattern in ponderosa pine forests. Ecology. 42(3): 493-499. [5780]
28. Coupland, Robert T. 1950. Ecology of mixed prairie in Canada. Ecological Monographs. 20(4): 271-315. [700]
29. Coxson, Darwyn S.; Looney, John Henry H. 1986. Vegetation patterns within southern Alberta coulees. Canadian Journal of Botany. 64: 2464-2475. [1957]
30. Damhoureyeh, Said A.; Harnett, David C. 2002. Variation in grazing tolerance among three tallgrass prairie plant species. American Journal of Botany. 89(10): 1634-1643. [44582]
31. Delaware Department of Natural Resources and Environmental Control, Division of Fish and Wildlife. 1999. Delaware Natural Heritage Program: Non-native plant species in Delaware, [Online]. Available: http://www.dnrec.state.de.us/fw/weeds.htm [2000, June 2]. [35346]
32. Dittberner, Phillip L.; Olson, Michael R. 1983. The plant information network (PIN) data base: Colorado, Montana, North Dakota, Utah, and Wyoming. FWS/OBS-83/86. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service. 786 p. [806]
33. Dorn, Robert D. 1984. Vascular plants of Montana. Cheyenne, WY: Mountain West Publishing. 276 p. [819]
34. Dorn, Robert D. 1988. Vascular plants of Wyoming. Cheyenne, WY: Mountain West Publishing. 340 p. [6129]
35. Duchesne, Luc C.; Hawkes, Brad C. 2000. Fire in northern ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 35-51. [36982]
36. Eddleman, Lee E. 1977. Indigenous plants of southeastern Montana. I. Viability and suitability for reclamation in the Fort Union Basin. Special Publication 4. Missoula, MT: University of Montana, School of Forestry, Montana Forest and Conservation Experiment Station. 122 p. [42440]
37. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905]
38. Farnsworth, Raymond B. 1975. Nitrogen fixation in shrubs. In: Stutz, Howard C., ed. Wildland shrubs: Symposium and workshop proceedings; 1975 November 5-7; Provo, UT. Provo, UT: Brigham Young University: 32-71. [909]
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