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Introductory

SPECIES: Agrostis scabra | Ticklegrass
ABBREVIATION : AGRSCA SYNONYMS : Agrostis hyemalis (Walt.) B.S.P. var. tenuis (Tuckerm.) Gl. Agrostis geminata Trin. Agrostis hyemalis Auct. SCS PLANT CODE : AGSC5 COMMON NAMES : ticklegrass hairgrass rough bentgrass winter bentgrass TAXONOMY : The currently accepted scientific name of ticklegrass is Agrostis scabra Willdenow [21,35,41,47]. It is also occasionally referred to as A. hyemalis Auct. (or other authorities) [2,17,18] but is considered to be specifically distinct from A. hyemalis (Walt.) B.S.P. The following varieties are recognized: Agrostis scabra var. geminata (Trin.) Swallen [16,21,30,42] Agrostis scabra var. septentrionalis Fern. [10,21,35,42] A. scabra hybridizes with A. stolonifera and A. exarata [47]. LIFE FORM : Graminoid FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Robin F. Matthews, May 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Matthews, Robin F. 1992. Agrostis scabra. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Agrostis scabra | Ticklegrass
GENERAL DISTRIBUTION : Ticklegrass is distributed throughout Alaska, the continental United States (but sparingly in the Southeast), Greenland, Canada, Mexico, and Asia [2,13,17,42,47]. ECOSYSTEMS : FRES10 White - red - jack pine FRES11 Spruce - fir FRES12 Longleaf - slash pine FRES13 Loblolly - shortleaf pine FRES17 Elm - ash - cottonwood FRES19 Aspen - birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES23 Fir - spruce FRES24 Hemlock - Sitka spruce FRES25 Larch FRES26 Lodgepole pine FRES28 Western hardwoods FRES29 Sagebrush FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES37 Mountain meadows FRES38 Plains grasslands FRES39 Prairie FRES40 Desert grasslands FRES41 Wet grasslands FRES42 Annual grasslands FRES44 Alpine STATES : AL AK AZ AR CA CO CT DE FL GA HI 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 WV WI WY AB BC LB MB NB NF NT NS ON PE PQ SK YT MEXICO ADMINISTRATIVE UNITS : ACAD BIHO BICA CACH CHIR CRMO CUVA DENA DETO FLFO GLBA GLAC GRCA GRTE GRSM INDU KICA LACL LAVO MORA MORU NOCA OLYM PIPE ROCR ROMO SAGU SEQU SHIL THRO TICA VOYA YELL YOSE YUCH ZION BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains 3 Southern Pacific Border 4 Sierra Mountains 5 Columbia Plateau 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 : K001 Spruce - cedar - hemlock forest K002 Cedar - hemlock - Douglas-fir forest K005 Mixed conifer forest K008 Lodgepole pine - subalpine forest K010 Ponderosa shrub forest K011 Western ponderosa forest K012 Douglas-fir forest K014 Grand fir - Douglas-fir forest K015 Western spruce - fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K019 Arizona pine forest K021 Southwestern spruce - fir forest K023 Juniper - pinyon woodland K026 Oregon oakwoods K037 Mountain-mahogany - oak scrub K038 Great Basin sagebrush K047 Fescue - oatgrass K048 California steppe K049 Tule marshes K050 Fescue - wheatgrass K051 Wheatgrass - bluegrass K052 Alpine meadows and barren K053 Grama - galleta steppe K054 Grama - tobosa prairie K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K057 Galleta - three-awn shrubsteppe K063 Foothills prairie K064 Grama - needlegrass - wheatgrass K065 Grama - buffalograss K066 Wheatgrass - needlegrass K067 Wheatgrass - bluestem - needlegrass K068 Wheatgrass - grama - buffalograss K069 Bluestem - grama prairie K070 Sandsage - bluestem prairie K074 Bluestem prairie K075 Nebraska Sandhills prairie K076 Blackland prairie K081 Oak savanna K084 Cross Timbers K093 Great Lakes spruce - fir forest K094 Conifer bog K095 Great Lakes pine forest K098 Northern floodplain forest K108 Northern hardwoods - spruce forest K110 Northeastern oak - pine forest K111 Oak - hickory - pine forest K112 Southern mixed forest SAF COVER TYPES : 1 Jack pine 5 Balsam fir 12 Black spruce 13 Black spruce - tamarack 15 Red pine 16 Aspen 18 Paper birch 38 Tamarack 69 Sand pine 70 Longleaf pine 80 Loblolly pine - shortleaf pine 81 Loblolly pine 107 White spruce 201 White spruce 202 White spruce - paper birch 204 Black spruce 210 Interior Douglas-fir 212 Western larch 216 Blue spruce 217 Aspen 218 Lodgepole pine 221 Red alder 222 Black cottonwood - willow 224 Western hemlock 225 Western hemlock - Sitka spruce 227 Western redcedar - western hemlock 228 Western redcedar 229 Pacific Douglas-fir 230 Douglas-fir - western hemlock 235 Cottonwood - willow 237 Interior ponderosa pine 239 Pinyon - juniper 244 Pacific ponderosa pine - Douglas-fir 245 Pacific ponderosa pine 251 White spruce - aspen 252 Paper birch 253 Black spruce - white spruce 254 Black spruce - paper birch SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Ticklegrass occurs throughout a wide variety of habitats and may be a dominant or codominant in moist meadows or on streambanks. Published classifications listing ticklegrass as a dominant component of plant associations (pas) or community types (cts) are as follows: AREA CLASSIFICATION AUTHORITY CA: Sequoia NP montane meadow pas Halpern 1986 ID: Upper Salmon/Middle riparian cts Tuhy & Jensen 1982 Fork Salmon River

VALUE AND USE

SPECIES: Agrostis scabra | Ticklegrass
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Although ticklegrass is a common and widespread species, the large ratio of seed head to foliage prevents it from being an important livestock forage plant. Prior to flowering, however, cattle, sheep, and horses readily consume it [32,41]. Ticklegrass is occasionally eaten by elk, mule deer, white-tail deer, pronghorn, small mammals, upland gamebirds, and waterfowl [8]. Moose may also graze on ticklegrass throughout the year [26]. PALATABILITY : Ticklegrass is considered to be relatively unpalatable to livestock but is consumed early in the season [32,33,41]. The relish and degree of use shown by livestock and wildlife in several western states is rated as follows [8]: UT WY MT ND Cattle good fair poor fair Sheep fair fair poor fair Horses fair fair poor fair Elk good good ---- ---- Mule deer fair poor ---- ---- White-tailed deer ---- poor ---- poor Pronghorn poor poor ---- poor Upland gamebirds poor fair ---- ---- Waterfowl poor poor ---- fair Small nongame birds poor fair ---- ---- Small mammals poor fair ---- ---- NUTRITIONAL VALUE : Ticklegrass has been rated as fair in energy value and low in protein value [8]. COVER VALUE : In certain areas, ticklegrass provides moderate cover for white-tailed deer, pronghorn, small mammals, upland gamebirds, and small nongame birds. It may also provide good cover for waterfowl [8]. VALUE FOR REHABILITATION OF DISTURBED SITES : Ticklegrass is a suitable candidate for revegetation programs, particularily in northern regions [43]. It has been used successfully in seeding experiments on alpine sites, where areas disturbed by grazing, recreation, and mining or mineral exploration are common [4]. Ticklegrass is also reported to be common on abandoned coal-mine sites in Alberta [37] and has colonized industrially damaged sites near Sudbury, Ontario [19]. It naturally invades areas damaged by sulfur emissions [48] and can be found on soils with copper concentrations of 450 p/m and nickel concentrations of 500 p/m [15]. In Yellowstone National Park, ticklegrass was seeded onto disturbed sites and after one growing season comprised 18 to 30 percent of the vegetation on test plots [29]. In revegetation trials in the Yukon Territory, seedlings emerged in the first growing season in 100 percent of seeded plots. All plots contained viable plants 7 years later. Eighty-six percent of plants produced seed in the second growing season, and all live plants produced seed during the seventh growing season [43]. In addition, ticklegrass has a fibrous root system that is effective in preventing soil erosion [8,15,48]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Ticklegrass is one of the most successful native grasses in the revegetation programs in which it has been included [29,43]. It has shown good potential for both short-term and long-term revegetation, and has low establishment requirements [8]. Ticklegrass seed is not available commercially, but it is produced at the Plant Materials Center in Bridger, Montana [4,29]. Seed can be collected at a rate of approximately 3.3 ounces per hour (95 g/hr) [29]. Ticklegrass produces lush growth in the first year if fertilized. In field trials near Tent Mountain, Alberta, it produced greater than 20 percent cover in fertilized plots in the first growing season [15]. In alpine areas, seeds should be planted in the fall to avoid breaking dormancy and to allow for optimal growth in the spring [29]. Ticklegrass is very effective at seed dispersal, and it is not necessary to plant seeds in areas where a source is nearby [15]. Ticklegrass increases in response to grazing [46]. Because the plant is not readily grazed after flowering, it is only utilized in the spring or early summer.

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Agrostis scabra | Ticklegrass
GENERAL BOTANICAL CHARACTERISTICS : Ticklegrass is a short-lived, perennial bunchgrass. Culms are slender and erect, and the basal leaves are often scabrous. The panicle is large and diffuse at maturity [1,10,30,47]. Ticklegrass is typically 6 to 39 inches (15-100 cm) tall [10,18,23] but often reaches 50 inches (130 cm) in height [31,32]. The plant has a fibrous root system [48] but is not rhizomatous [31]. Ticklegrass is often confused with winter bentgrass (A. hyemalis (Walt.) B.S.P.), but the latter generally flowers earlier [13]. RAUNKIAER LIFE FORM : Hemicryptophyte REGENERATION PROCESSES : Ticklegrass reproduces primarly by seed but can spread laterally by stolons. The diffuse inflorescence breaks away at maturity and can be dispersed over long distances by wind [15]. Seeds colonize recently disturbed sites with exposed mineral soil seedbeds [22]. SITE CHARACTERISTICS : Ticklegrass occurs throughout a wide variety of habitats including woodlands, forest openings, grasslands, shrublands, meadows, swamps, bogs, marshes, and stream and lake margins [5,6,24,47]. It also grows on disturbed sites, such as in ditches or along roadsides, and in pastures or abandoned fields [14,24,28]. Ticklegrass occurs from sea level to alpine zones [4,15,17]. It occupies sites as high as 12,000 feet (3,600 m) in Colorado [8]. Ticklegrass is tolerant of a wide range of moisture regimes; it thrives in wet or moist soils and can survive seasonal stem submergence [13,15,41]. Ticklegrass is also found in dry habitats and is a common component of semiarid grasslands and sagebrush communities [8,10,15,18]. Ticklegrass grows well on sandy loam, loam, and clay loam soil textures [8]. It is adapted to soils that are low in nutrients and is tolerant of low pH levels [15]. Ticklegrass shows poor growth in sodic soils [8]. SUCCESSIONAL STATUS : Facultative Seral Species Ticklegrass is generally a pioneer or invader species [11,15,22]. It is relatively shade intolerant, and thrives in open, sunny locations [15]. Seed is widely dispersed by wind and requires bare mineral soil for establishment; seedlings are common on recently disturbed sites [15,22]. Ticklegrass has invaded abandoned fields throughout prairie regions, and barren sandy soils near Coniston, Ontario. It is a pioneer of dry white spruce (Picea glauca) sites near Norman Wells, Northwest Territories [15], and clearcut jack pine (Pinus banksiana) sites in Saskatchewan [7]. Once ticklegrass becomes established, it may remain important throughout the early seral stages [22]. In boreal forest floodplain succession, ticklegrass invades initially, and then endures through the early willow stages [25,44]. Ticklegrass is also a component of near climax range communities in Montana [36]. In the Sierra Nevada, California, ticklegrass is an increaser species in climax meadow vegetation [33]. SEASONAL DEVELOPMENT : Ticklegrass flowers from June to September, depending on location [8,10,13]. Seed is shed in late summer [41].

FIRE ECOLOGY

SPECIES: Agrostis scabra | Ticklegrass
FIRE ECOLOGY OR ADAPTATIONS : Wind-dispersed ticklegrass seeds readily colonize bare mineral soil on recently burned sites [6,20,38]. Seeds may also be stored for short durations in the soil, allowing for early establishment of areas burned in the spring [11]. POSTFIRE REGENERATION STRATEGY : Tussock graminoid Initial-offsite colonizer (off-site, initial community)

FIRE EFFECTS

SPECIES: Agrostis scabra | Ticklegrass
IMMEDIATE FIRE EFFECT ON PLANT : Fire generally top-kills ticklegrass. Specific effects on ticklegrass mortality, however, are not well documented. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : In general, ticklegrass increases in abundance in response to fire. Seedlings immediately colonize recently burned areas, provided a favorable seedbed has been established [27,39]. Annual spring burns in aspen stands in Alberta caused an increase in ticklegrass inflorescence production. In unburned areas, there was an average of one flower head per square foot (10/sq m), but on burned sites 10 flower heads per square foot (110/sq.m) were produced [2]. In interior Alaska, seedlings were not found in burned plots where the organic layer had not been completely removed, although a seed source was nearby. Seedlings were, however, abundant on adjacent firelines [45]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Agrostis scabra | Ticklegrass
REFERENCES : 1. Anderson, Howard G.; Bailey, Arthur W. 1980. Effects of annual burning on grassland in the aspen parkland of east-central Alberta. Canadian Journal of Botany. 58: 985-996. [3499] 2. Anderson, J. P. 1959. Flora of Alaska and adjacent parts of Canada. Ames, IA: Iowa State University Press. 543 p. [9928] 3. 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] 4. Brown, Ray W.; Johnston, Robert S. 1979. Revegetation of disturbed alpine rangelands. In: Johnson, D. A., ed. Special management needs of alpine ecosystems. Range Science Series No. 5. Denver, CO: Society for Range Management: 76-94. [188] 5. Calmes, Mary A. 1976. Vegetation pattern of bottomland bogs in the Fairbanks area, Alaska. Fairbanks, AK: University of Alaska. 104 p. Thesis. [14785] 6. Carroll, S. B.; Bliss, L. C. 1982. Jack pine - lichen woodland on sandy soils in northern Saskatchewan and northeastern Alberta. Canadian Journal of Botany. 60: 2270-2282. [7283] 7. Chrosciewicz, Z. 1983. Jack pine regeneration following postcut burning and seeding in central Saskatchewan. Information Report NOR-X-253. Edmonton, AB: Environment Canada, Canadian Forestry Service, Northern Forest Research Centre. 11 p. [16916] 8. 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] 9. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 10. Fernald, Merritt Lyndon. 1950. Gray's manual of botany. [Corrections supplied by R. C. Rollins]. Portland, OR: Dioscorides Press. 1632 p. (Dudley, Theodore R., gen. ed.; Biosystematics, Floristic & Phylogeny Series; vol. 2). [14935] 11. Fyles, James W. 1989. Seed bank populations in upland coniferous forests in central Alberta. Canadian Journal of Botany. 67: 274-278. [6388] 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. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 14. Halpern, Charles B. 1986. Montane meadow plant associations of Sequoia National Park, California. Madrono. 33(1): 1-23. [1067] 15. Hardy BBT Limited. 1989. Manual of plant species suitability for reclamation in Alberta. 2d ed. Report No. RRTAC 89-4. Edmonton, AB: Alberta Land Conservation and Reclamation Council. 436 p. [15460] 16. Hitchcock, A. S. 1951. Manual of the grasses of the United States. Misc. Publ. No. 200. Washington, DC: U.S. Department of Agriculture, Agricultural Research Administration. 1051 p. [2nd edition revised by Agnes Chase in two volumes. New York: Dover Publications, Inc.]. [1165] 17. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 18. Hulten, Eric. 1968. Flora of Alaska and neighboring territories. Stanford, CA: Stanford University Press. 1008 p. [13403] 19. James, G. I.; Courtin, G. M. 1985. Stand structure and growth form of the birch transition community in an industrially damaged ecosystem, Sudbury, Ontario. Canadian Journal of Forest Research. 15(5): 809-817. [12630] 20. Johnson, E. A. 1975. Buried seed populations in the subarctic forest east of Great Slave Lake, Northwest Territories. Canadian Journal of Botany. 53: 2933-2941. [6466] 21. 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] 22. Klinka, K.; Scagel, A. M.; Courtin, P. J. 1985. Vegetation relationships among some seral ecosystems in southwestern British Columbia. Canadian Journal of Forestry. 15: 561-569. [5985] 23. Kuchler, A. W. 1964. Manual to accompany the map of potential vegetation of the conterminous United States. Special Publication No. 36. New York: American Geographical Society. 77 p. [1384] 24. Lackschewitz, Klaus. 1991. Vascular plants of west-central Montana--identification guidebook. Gen. Tech. Rep. INT-227. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 648 p. [13798] 25. LeResche, R. E.; Bishop, R. H.; Coady, J. W. 1974. Distribution and habitats of moose in Alaska. Le Naturaliste Canadien. 101: 143-178. [15190] 26. LeResche, Robert E.; Davis, James L. 1973. Importance of nonbrowse foods to moose on the Kenai Peninsula, Alaska. Journal of Wildlife Management. 37(3): 279-287. [13123] 27. Lutz, H. J. 1956. Ecological effects of forest fires in the interior of Alaska. Tech. Bull. No. 1133. Washington, DC: U.S. Department of Agriculture, Forest Service. 121 p. [7653] 28. Lyon, L. Jack; Stickney, Peter F. 1976. Early vegetal succession following large northern Rocky Mountain wildfires. In: Proceedings, Tall Timbers fire ecology conference and Intermountain Fire Research Council fire and land management symposium; 1974 October 8-10; Missoula, MT. No. 14. Tallahassee, FL: Tall Timbers Research Station: 355-373. [1496] 29. Majerus, Mark E. 1991. Yellowstone National Park-Bridger Plant Marterials Center native plant program. In: Rangeland Technology Equipment Council, 1991 annual report. 9222-2808-MTDC. Washington, DC: U.S. Department of Agriculture, Forest Service, Technology and Development Program: 17-22. [17082] 30. Mason, Herbert L. 1957. A flora of the marshes of California. Berkeley, CA: University of California Press. 878 p. [16905] 31. May, Morton. 1960. Key to the major grasses of the Big Horn Mountains based on vegetative characters. Bulletin 371. Laramie, WY: University of Wyoming, Agricultural Experiment Station. 44 p. [3236] 32. Morris, H. E.; Booth, W. E.; Payne, G. F.; Stitt, R. E. 1950. Important grasses on Montana ranges. Bull. No. 470. Bozeman, MT: Montana Agricultural Experiment Station. 52 p. [5520] 33. Ratliff, Raymond D. 1982. A meadow site classification for the Sierra Nevada, California. Gen. Tech. Rep. PSW-60. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station. 16 p. [1941] 34. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 35. Roland, A. E.; Smith, E. C. 1969. The flora of Nova Scotia. Halifax, NS: Nova Scotia Museum. 746 p. [13158] 36. Ross, Robert L.; Murray, Earl P.; Haigh, June G. 1973. Soil and vegetation inventory of near-pristine sites in Montana. Bozeman, MT: U.S. Department of Agriculture, Soil Conservation Service. 55 p. [2029] 37. Russell, W. B. 1985. Vascular flora of abandoned coal-mined land, Rocky Mountain Foothills, Alberta. Canadian Field-Naturalist. 99(4): 503-516. [10461] 38. Smith, D. W. 1970. Concentrations of soil nutrients before and after fire. Canadian Journal of Soil Science. 50: 17-29. [8534] 39. Stickney, Peter F. 1985. Data base for early postfire succession on the Sundance Burn, northern Idaho. Gen. Tech. Rep. INT-189. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 121 p. [7223] 40. Tuhy, Joel S.; Jensen, Sherman. 1982. Riparian classification for the Upper Salmon/Middle Fork Salmon River drainages, Idaho. Smithfield, UT: White Horse Associates. Final Report, Contract with U.S.S. Forest Service, Region 4. 153 p. [8380] 41. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 42. U.S. Department of Agriculture, Soil Conservation Service. 1982. National list of scientific plant names. Vol. 1. List of plant names. SCS-TP-159. Washington, DC. 416 p. [11573] 43. Vaartnou, Manivalde. 1988. The potential of native populations of grasses in northern revegetation. In: Kershaw, Peter, ed. Northern environmental disturbances. Occas. Publ. No. 24. Edmonton, AB: University of Alberta, Boreal Institute for Northern Studies: 31-41. [14418] 44. Viereck, Leslie A. 1970. Forest succession and soil development adjacent to the Chena River in interior Alaska. Arctic and Alpine Research. 2(1): 1-26. [12466] 45. Viereck, Leslie A. 1982. Effects of fire and firelines on active layer thickness and soil temperatures in interior Alaska. In: Proceedings, 4th Canadian permafrost conference; 1981 March 2-6; Calgary, AB. The Roger J.E. Brown Memorial Volume. Ottawa, ON: National Research Council of Canada: 123-135. [7303] 46. Wambolt, Carl. 1981. Montana range plants: Common and scientific names. Bulletin 355. Bozeman, MT: Montana State University, Cooperative Extension Service. 27 p. [2450] 47. 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] 48. Winterhalder, Keith. 1990. The trigger-factor approach to the initiation of natural regeneration of plant communities on industrially-damaged lands at Sudbury, Ontario. In: Hughes, H. Glenn; Bonnicksen, Thomas M., eds. Restoration '89: the new management challenge: Proceedings, 1st annual meeting of the Society for Ecological Restoration; 1989 January 16-20; Oakland, CA. Madison, WI: The University of Wisconsin Arboretum, Society for Ecological Restoration: 215-226. [14697] 49. 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]

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