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Introductory

SPECIES: Leptodactylon pungens | Prickly Phlox
ABBREVIATION : LEPPUN SYNONYMS : Gilia pungens SCS PLANT CODE : LEPU COMMON NAMES : prickly phlox gilia granite prickly phlox granite-gilia rock gilia granite prickly gilia TAXONOMY : The fully documented species name is Leptodactylon pungens (Torr.) Nutt. Cronquist and others [5] recognize the following varieties: Leptodactylon pungens var. pungens Leptodactylon pungens var. hallii (Parish) Jepson LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : J. L. Holifield, March 1988 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Holifield, Jennifer L. 1988. Leptodactylon pungens. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Leptodactylon pungens | Prickly Phlox
GENERAL DISTRIBUTION : Prickly phlox occurs east of the Cascade Mountains in Washington and adjacent southern British Columbia eastward to Montana, and extends south to northern Baja California, Arizona, New Mexico, and central Nebraska [5]. ECOSYSTEMS : FRES20 Douglas-fir FRES21 Ponderosa pine FRES23 Fir - spruce FRES29 Sagebrush FRES30 Desert shrub FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper STATES : AZ CA CO ID MT NE NM NV OR UT WA WY BC ADMINISTRATIVE UNITS : BICA BRCA CARE COLM CRLA DEVA DINO FOBU GLCA GRTE GRBA GRSA JODA LABE MEVE NABR YELL ZION BLM PHYSIOGRAPHIC REGIONS : 2 Cascade Mountains 4 Sierra Mountains 5 Columbia Plateau 6 Upper Basin and Range 7 Lower Basin and Range 8 Northern Rocky Mountains 11 Southern Rocky Mountains 12 Colorado Plateau KUCHLER PLANT ASSOCIATIONS : K011 Western ponderosa forest K012 Douglas-fir forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K019 Arizona pine forest K021 Southwestern spruce - fir forest K023 Juniper - pinyon woodland K037 Mountain mahogany - oak scrub K038 Great Basin sagebrush K040 Saltbush - greasewood K051 Wheatgrass - bluegrass K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K057 Galleta - three-awn shrubsteppe K063 Foothills prairie K065 Grama - buffalograss K066 Wheatgrass - needlegrass SAF COVER TYPES : 208 Whitebark pine 209 Bristlecone pine 219 Limber pine 237 Interior ponderosa pine 239 Pinyon - juniper 247 Jeffrey pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Prickly phlox occurs in sagebrush-grass, pinyon-juniper, Great Basin bristlecone pine (Pinus longaeva), limber pine (P. flexilis), white fir (Abies concolor), Jeffrey pine (Pinus jeffreyi), and whitebark pine (P. albicaulis) habitat types within its range. Prickly phlox is often a constituent of seral plant communities [11]. It has been described as an indicator of sites in poor condition [29].

VALUE AND USE

SPECIES: Leptodactylon pungens | Prickly Phlox
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Prickly phlox was used by bighorn sheep in December and by mule deer in February and April on bighorn sheep range in east-central Idaho [17]. In southeastern Idaho, prickly phlox is moderately grazed by sheep in early and late summer [14]. PALATABILITY : The degree of use shown by livestock and wildlife species for prickly phlox in several western states is rated as follows [6]: CO UT WY Cattle Poor Poor Poor Sheep Poor Poor Fair Horses Poor Poor Poor Pronghorn ---- Fair ---- Elk ---- Poor ---- Mule deer ---- Poor ---- Small mammals ---- Fair ---- Small nongame birds ---- Fair ---- Upland game birds ---- Fair ---- Waterfowl ---- Poor ---- NUTRITIONAL VALUE : Prickly phlox is rated poor in energy and protein value [6]. COVER VALUE : The degree to which prickly phlox provides environmental protection during one or more seasons for wildlife species in Utah is as follows [6]: Pronghorn Poor Elk Poor Mule deer Poor Small mammals Fair Small nongame birds Poor Upland game birds Poor Waterfowl Poor VALUE FOR REHABILITATION OF DISTURBED SITES : Prickly phlox is described as having low to moderate establishment requirements and low potential for biomass production [6]. It is rated as having low potential for erosion control and for short- and long-term revegetation projects [6]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Prickly phlox frequency has been reported to decrease with livestock exclusion [1,13]. On a southeastern Idaho sagebrush-grass range, Harniss and Wright [14] found a decrease in percent production of prickly phlox the first 2 years from early summer and late summer grazing by sheep. West and others [32] reported prickly phlox lives much longer on ungrazed plots. In areas in Utah where 2,4 D application had removed the shrub canopy, prickly phlox increased in density by seedling establishment within 4 years. However, it increased only at sites where cheatgrass (Bromus tectorum) did not increase and the remaining perennial grasses were not abundant [35].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Leptodactylon pungens | Prickly Phlox
GENERAL BOTANICAL CHARACTERISTICS : Prickly phlox is a native, perennial shrub or subshrub with a taproot [5,24]. It is more or less erect, open or densely branched, and ranges from 4 to 24 inches (1-6 dm) in height [5,15]. The plant is somewhat aromatic [5]. Herbage is puberulent to glandular-puberulent or glandular-villous to glabrous [31]. The numerous and crowded leaves are alternate to subopposite (or the lower are opposite) and are cleft into three to nine rigid, spinulose-tipped segments [5,31]. Dead leaves commonly persist through one or more seasons [5]. The sessile flowers of prickly phlox are solitary and auxillary or are at the ends of short leafy branches [5]. Flowers are usually dull white or cream colored and marked or washed with pale lavender outside but can vary to yellowish or salmon colored [5,31]. Flowers are nocturnal [5]. The seed capsule is usually three-loculed and persists for some time after seed dehiscence [5,31]. RAUNKIAER LIFE FORM : Undisturbed State: Chamaephyte Burned or Clipped State: Chamaephyte REGENERATION PROCESSES : Little information could be located in the available literature concerning the regenerative characteristics of prickly phlox. Its fruit is usually a three-loculed capsule which splits open at maturity to release the small seeds [5,19]. SITE CHARACTERISTICS : Prickly phlox grows on relatively open sites from the deserts, plains, valleys, and foothills to timberline or above in the drier mountains [5]. It occurs on alluvial terraces and fans, drainage bottoms, flats and gently rolling slopes to ridgetops in hilly and mountainous terrain [3,18,28,29,36]. Soil surface horizons are often coarse to cobbly and stoney, sandy or sandy loam in texture [9,11,18,29]. Soils are frequently granitic in origin, but prickly phlox also occurs on soils derived from colluvial and residual gneissic and schistic rock, sandstone, dolomite, limestone, and pumice [9,28,29,31]. Generalized elevational ranges for prickly phlox in several western states are reported as follows [3,6,18,21,25,28,29,36]: from 4,101 to 12,000 ft (1,250-3,658 m) in CA 4,000 to 9,500 ft (1,219-2,896 m) in CO 6,200 to 7,500 ft (1,890-2,286 m) in MT 4,593 to 12,000 ft (1,400-3,658 m) in NV 4,800 to 4,900 ft (1,463-1,493 m) in OR 4,500 to 8,600 ft (1,372-2,621 m) in UT 4,100 to 8,100 ft (1,250-2,469 m) in WY Elevational range for ssp. halli in California is reported to be 4,000 to 9,000 feet (1,219-3,658 m) [21]. Prickly phlox is typically not an abundant part of the vegetation [5]. It commonly occurs with such species as needle-and-thread grass (Stipa spp.), cheatgrass, bluebunch wheatgrass (Pseudoroegneria spicata), thread-leaf sedge (Carex filifolia), sandwort (Arenaria kingi), sulfur buckwheat (Eriogonum umbellatum), longleaf phlox (Phlox longifolia), rabbitbrush (Chrysothamnus spp.), snakeweed (Gutierrezia sarothrae), prickly pear (Opuntia polyacantha), bottlebrush squirreltail (Elymus elymoides), wax current (Ribes cereum), bitterbrush (Purshia tridentata), oak (Quercus turbinella), big sagebrush (Artemisia tridentata), and black sagebrush (A. nova) [2,3,18,24,26,28,32,35]. SUCCESSIONAL STATUS : In southern Idaho, Eggler [8] described prickly phlox as a dominant shrub on old, soil-covered volcanic flows. SEASONAL DEVELOPMENT : General flowering dates for prickly phlox in four western states are [6]: Beginning of Flowering Flowering End of Flowering CO May June August MT June July July WY May June July UT May ____ June In southern Idaho, Eggler [8] reported growth of prickly phlox ceased early in August.

FIRE ECOLOGY

SPECIES: Leptodactylon pungens | Prickly Phlox
FIRE ECOLOGY OR ADAPTATIONS : Prickly phlox is described as being severely damaged by fire [34]. POSTFIRE REGENERATION STRATEGY : NO-ENTRY

FIRE EFFECTS

SPECIES: Leptodactylon pungens | Prickly Phlox
IMMEDIATE FIRE EFFECT ON PLANT : Prickly phlox is severely damaged by fire [34]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : In sagebrush-grass vegetation of the Great Basin area of Utah, West and Hassan [32] reported the percent cover of prickly phlox initially decreased after a July wildfire. For four macroplots sampled before and after the wildfire, the mean (kg/ha) and one standard error of mean (within parenthesis) for prickly phlox were as follows [32]: 1981 1982 1983 (before fire) LEPPUN 8.08 (23.10) 0.78 (2.62) 3.32 (8.92) In western Nevada, prickly phlox increased in density after burning [35]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Leptodactylon pungens | Prickly Phlox
REFERENCES : 1. Bethlenfalvay, Gabor J.; Dakessian, Suren. 1984. Grazing effects on mycorrhizal colonization and floristic composition of the vegetation on a semiarid range in nothern Nevada. Journal of Range Management. 37(4): 312-316. [439] 2. Blackburn, Wilbert H.; Eckert, Richard E., Jr.; Tueller, Paul T. 1969. Vegetation and soils of the Coils Creek Watershed. R-48. Reno, NV: University of Nevada, Agricultural Experiment Station. 80 p. In cooperation with: U.S. Department of the Interior, Bureau of Land Management. [455] 3. Blackburn, Wilbert H.; Eckert, Richard E., Jr.; Tueller, Paul T. 1969. Vegetation and soils of the Crane Springs Watershed. R-55. Reno, NV: University of Nevada, Agricultural Experiment Station. 65 p. In cooperation with: U.S. Department of the Interior, Burearu of Land Management. [456] 4. Blackburn, Wilbert H.; Eckert, Richard E., Jr.; Tueller, Paul T. 1971. Vegetation and soils of the Rock Springs Watershed. R-83. Reno, NV: University of Nevada, Agricultural Experiment Station. 116 p. In cooperation with: U.S. Department of the Interior, Bureau of Land Management. [457] 5. Cronquist, Arthur; Holmgren, Arthur H.; Holmgren, Noel H.; [and others]. 1977. Intermountain flora: Vascular plants of the Intermountain West, U.S.A. Vol. 6. The Monocotyledons. New York: Columbia University Press. 584 p. [719] 6. 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] 7. Eckert, Richard E., Jr. 1957. Vegetation-soil relationships in some Artemisia types in northern Harney and Lake Counties. Corvallis, OR: Oregon State College. 208 p. Dissertation. [837] 8. Eggler, Willis A. 1941. Primary succession on volcanic deposits in southern Idaho. Ecological Monographs. 11: 277-298. [852] 9. Erhard, Dean H. 1979. Plant communities and habitat types in the Lava Beds National Monument, California. Corvallis, OR: Oregon State University. 173 p. Thesis. [869] 10. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 11. Francis, Richard E. 1986. Phyto-edaphic communities of the Upper Rio Puerco Watershed, New Mexico. Res. Pap. RM-272. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 73 p. [954] 12. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; [and others]. 1977. Vegetation and environmental features of forest and range ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of Agriculture, Forest Service. 68 p. [998] 13. Harniss, Roy O.; West, Neil E. 1973. Changes in Artemisia tridentata/Sitanion hystrix vegetation on the National Reactor Testing Station, southeastern Idaho, 1950-1965. Utah Academy Proceedings. 50(1): 10-16. [1087] 14. Harniss, R. O.; Wright, H. A. 1982. Summer grazing of sagebrush-grass range by sheep. Journal of Range Management. 35(1): 13-17. [3729] 15. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press Inc. 666 p. [6851] 16. Kartesz, John T.; Kartesz, Rosemarie. 1980. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. Volume II: The biota of North America. Chapel Hill, NC: The University of North Carolina Press; in confederation with Anne H. Lindsey and C. Richie Bell, North Carolina Botanical Garden. 500 p. [6954] 17. Lauer, Jerry L.; Peek, James M. 1976. Big game-livestock relationships on the bighorn sheep winter range, East Fork Salmon River, Idaho. Bulletin No. 12. Moscow, ID: University of Idaho Forest, Wildlife and Range Experiment Station. 44 p. [1417] 18. Lewis, Mont E. 1971. Flora and major plant communities of the Ruby-East Humboldt Mountains with special emphasis on Lamoille Canyon. Elko, NV: U.S. Department of Agriculture, Forest Service, Region 4, Humboldt National Forest. 62 p. [1450] 19. Mozingo, Hugh N. 1987. Shrubs of the Great Basin: A natural history. Reno, NV: University of Nevada Press. 342 p. [1702] 20. Mueggler, W. F.; Stewart, W. L. 1980. Grassland and shrubland habitat types of western Montana. Gen. Tech. Rep. INT-66. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 154 p. [1717] 21. Munz, Philip A. 1973. A California flora and supplement. Berkeley, CA: University of California Press. 1905 p. [6155] 22. Passey, H. B.; Hugie, Vern K.; Williams, E. W.; Ball, D. E. 1982. Relationships between soil, plant community, and climate on rangelands of the Intermountain West. Tech. Bull. 1669. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 123 p. [1834] 23. Peek, James M.; Riggs, Robert A.; Lauer, Jerry L. 1979. Evaluation of fall burning on bighorn sheep winter range. Journal of Range Management. 32(6): 430-432. [1863] 24. Smith, P. Dean; Edell, Jack; Jurak, Frank; Young, James. 1978. Rehabilitation of eastern Nevada roadsides. California Agriculture. April: 4-5. [2177] 25. Stark, N. 1966. Review of highway planting information appropriate to Nevada. Bull. No. B-7. Reno, NV: University of Nevada, College of Agriculture, Desert Research Institute. 209 p. In cooperation with: Nevada State Highway Department. [47] 26. Thorne, Robert F. 1976. The vascular plant communities of California. In: Latting, June, ed. Symposium proceedings: plant communities of southern California; 1974 May 4; Fullerton, CA. Special Publication No. 2. Berkeley, CA: California Native Plant Society: 1-31. [3289] 27. Tueller, Paul Teuscher. 1962. Plant succession on two Artemisia habitat types in southeastern Oregon. Corvallis, OR: Oregon State University. 249 p. Thesis. [2366] 28. Vasek, Frank C.; Thorne, Robert F. 1977. Transmontane coniferous vegetation. In: Barbour, Michael G.; Major, Jack, eds. Terrestrial vegetation of California. New York: John Wiley & Sons: 797-832. [4265] 29. Volland, Leonard A. 1985. Plant associations of the central Oregon Pumice Zone. Rt-ECOL-104-1985. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 138 p. [7341] 30. Vories, Kimery C. 1981. Growing Colorado plants from seed: a state of the art. Volume I. Shrubs. Gen. Tech. Rep. INT-103. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 80 p. [3426] 31. Welsh, Stanley L.; Atwood, N. Duane; Goodrich, Sherel; Higgins, Larry C., eds. 1987. A Utah flora. Great Basin Naturalist Memoir No. 9. Provo, UT: Brigham Young University. 894 p. [2944] 32. West, Neil E.; Hassan, M. A. 1985. Recovery of sagebrush-grass vegetation following wildfire. Journal of Range Management. 38(2): 131-134. [2513] 33. West, Neil E.; Rea, Kenneth H.; Harniss, Roy O. 1979. Plant demographic studies in sagebrush-grass communities of southeastern Idaho. Ecology. 60(2): 376-388. [2515] 34. Wright, Henry A.; Bailey, Arthur W. 1982. Fire ecology: United States and southern Canada. New York: John Wiley & Sons. 501 p. [2620] 35. Young, James A.; Evans, Raymond A. 1974. Population dynamics of green rabbitbrush in disturbed big sagebrush communities. Journal of Range Management. 27(2): 127-132. [2652] 36. Zamora, B.; Tueller, Paul T. 1973. Artemisia arbuscula, A. longiloba, and A. nova habitat types in northern Nevada. Great Basin Naturalist. 33(4): 225-242. [2688] 37. Stickney, Peter F. 1989. Seral origin of species originating in northern Rocky Mountain forests. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT; RWU 4403 files. 7 p. [20090] 38. U.S. Department of Agriculture, Soil Conservation Service. 1994. Plants of the U.S.--alphabetical listing. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 954 p. [23104] 39. U.S. Department of the Interior, National Biological Survey. [n.d.]. NP Flora [Data base]. Davis, CA: U.S. Department of the Interior, National Biological Survey. [23119]

Index

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