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Introductory

SPECIES: Atriplex canescens | Fourwing Saltbush
ABBREVIATION : ATRCAN SYNONYMS : Atriplex occidentalis Atriplex tetraptera Atriplex nuttallii Obione canescens Obione occidentalis Obione tetraptera Pterchiton canescens Pterchiton occidentalis SCS PLANT CODE : ATCA2 COMMON NAMES : fourwing saltbush wingscale hoary saltbush shadscale chamiza buckwheat shrub cenizo bushy atriplex salt sage wafer sage TAXONOMY : The fully documented scientific name of fourwing saltbush is Atriplex canescens (Pursh) Nutt. [18]. Commonly recognized subspecies and varieties are as follows [18]: Atriplex canescens ssp. aptera (A. Nels.) Hall & Clements Atriplex canescens ssp. canescens Atriplex canescens ssp. canescens var. canescens Atriplex canescens ssp. canescens var. laciniata Parish Fourwing saltbush is one of the most variable and rapidly evolving species in North America [53]. Numerous ecotypes, races, varieties, and forms have been described. Mutations, alloploidy, and autoploidy are common. Both diploid and polyploid (2n, 4n, 6n, 10n, 12n) races have been described, and hybridization with other saltbush species is common. Natural hybrids occur between fourwing saltbush and twelve other species of saltbush (Atriplex spp.) including Atriplex tridentata, shadscale (A. confertifolia), mound saltbush (A. obovata), Castle Valley clover (A. cuneata), saltsage (A. gardneri), A. falcata, allscale saltbush (A. polycarpa), and A. garrettii [51,52,53]. Artificial hybrids with spiny hopsage (Grayia spinosa), spineless hopsage (G. brandegi), and black greasewood (Sarcobatus vermiculatus) have also been produced [39]. Fourwing saltbush x Atriplex tridentata hybrids are very common throughout Utah [52]. Saltsage x fourwing saltbush hybrids are widespread in northern Wyoming and southern Montana and form populations which have been delineated as the subspecies A. canescens ssp. aptera (aptera fourwing saltbush). Some taxonomists prefer to recognize this entity as a separate species, A. aptera [52]. Products of fourwing saltbush x A. falcata crosses have been designated "A. bonnevillensis" by some taxonomists, and products of hybridization with allscale saltbush have been delineated as "A. laciniata" [52]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : NO-ENTRY OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : D. Tirmenstein, November 1986. LAST REVISED BY AND DATE : D. Tirmenstein, September 1990 AUTHORSHIP AND CITATION : Tirmenstein, Debra A. 1986. Atriplex canescens. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Atriplex canescens | Fourwing Saltbush
GENERAL DISTRIBUTION : Fourwing saltbush is widely distributed throughout the western United States from the Pacific Coast Ranges to the Great Plains [25]. It extends from northern Mexico to southern Canada [36]. Diploids occur most commonly in Mexico, New Mexico, and southern Arizona, with an isolated population in the Little Sahara Sand Dunes of central Utah [53]. Tetraploids are widely distributed and hexaploids reach greatest abundance in Nevada [53]. Decaploids and 12ploids grow in southern California, Baja California, and northwestern Mexico [53]. ECOSYSTEMS : FRES17 Elm - ash - cottonwood FRES21 Ponderosa pine FRES29 Sagebrush FRES30 Desert shrub FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES38 Plains grasslands FRES39 Prairie FRES40 Desert grasslands STATES : AZ CA CO ID KS MT ND NE NM NV OK OR SD TX UT WA WY AB MB MEXICO ADMINISTRATIVE UNITS : ARCH BADL BAND BIBE BICA BRCA CACH CANY CARE CACA CHCU COLM DEVA DINO FOBO GLCA GRCA GRSA GUMO JOTR LAMR MEVE MOCA NABR ORPI PEFO SAGU SCBL TICA WACA WHSA WICA WUPA YELL 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 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K016 Eastern ponderosa forest K019 Arizona pine forest K023 Juniper - pinyon woodland K037 Mountain mahogany - oak scrub K038 Great Basin sagebrush K039 Blackbrush K040 Saltbush - greasewood K041 Creosotebush K044 Creosotebush - tarbush K051 Wheatgrass - needlegrass shrubsteppe K053 Grama - galleta steppe K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K057 Galleta - three-awn shrubsteppe K063 Foothills prairie K064 Grama - needlegrass - wheatgrass K066 Wheatgrass - needlegrass K067 Wheatgrass - bluestem prairie K070 Sandsage - bluestem prairie K075 Nebraska Sandhills prairie K098 Northern floodplain forest SAF COVER TYPES : 237 Interior ponderosa pine 238 Western juniper 239 Pinyon - juniper SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Fourwing saltbush occurs as an understory species in many Great Basin conifer forests, pinyon (Pinus spp.)-juniper (Juniperus spp.) woodlands, northern and southern desert shrublands, Mohave and Sonoran desert scrub, and salt desert scrub communities [29,56,62]. It is seldom found in pure stands, but grows as a dominant or codominant species in a number of saltbush-grassland communities. Common codominants or associates include blue grama (Bouteloua gracilis), black grama (B. eriopoda), galleta (Hilaria jamesii), alkali sacaton (Sporobolus airoides) and other dropseeds (Sporobolus spp.), bottlebrush squirreltail (Elymus elymoides), western wheatgrass (Pascopyrum smithii), Indian ricegrass (Oryzopsis hymenoides), rubber rabbitbrush (Chrysothamnus nauseosus), black greasewood (Sarcobatus vermiculatus), black sagebrush (Artemisia nova), and broom snakeweed (Gutierrezia sarothrae) [14,59,62]. Fourwing saltbush is listed as a dominant or indicator species in the following publications: Phyto-edaphic communities of the Upper Rio Puerco Watershed, New Mexico [10] Preliminary habitat types of a semiarid grassland [11] Plant associations of Region Two: Potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas [17] A series of vegetation classification of Region 3 [28]

VALUE AND USE

SPECIES: Atriplex canescens | Fourwing Saltbush
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Fourwing saltbush is a valuable browse for many wildlife species and for domestic livestock. However, significant variation exists in palatability and nutritional levels of individuals and populations of fourwing saltbush [27]. Consumption varies annually and may be related to differences in salinity of the foliage [59]. Research indicates that some browsers such as jackrabbits may show a preference for either pistillate or staminate plants [67]. On many cold desert sites, accessions in which leaves and seed persist are browsed heavily during fall and winter months [37,39]. Leaves usually remain succulent during the hot, dry summer months and can provide some forage even in years when annuals fail. Fourwing saltbush generally provides good deer browse during all seasons and is used by elk in winter [59]. Pronghorns may feed on this shrub to some extent during all seasons of the year [71]. Fourwing saltbush is a preferred browse of many rabbits and small mammals [39]. Seeds are readily eaten by upland game birds, small nongame birds, and rodents [39]. Fourwing saltbush has fair to good forage value for domestic sheep and goats, and at least fair forage value for cattle [37]. In some areas, leaves and twigs are consumed "in quantity" by cattle during the spring and summer [25]. On rare occasions, fourwing saltbush has caused scours, bloat, and anemia in domestic livestock [59]. PALATABILITY : Fourwing saltbush is palatable to livestock, pronghorn, and deer in all seasons, and to elk in fall and winter [59]. However, palatability varies seasonally and annually [27]. Seeds and, in some instances, foliage are also preferred by many species of upland game birds, small nongame birds, rodents, and lagomorphs [39]. Palatability has been rated as follows [7,57]: CO MT OR UT WY Cattle Fair Fair ---- Fair Fair Sheep Good Good ---- Good Good Horses Fair Fair ---- Fair Good Pronghorns Good Poor ---- Good Good Bighorn ---- ---- Fair ---- ---- Elk Good ---- ---- Fair Poor Mule deer Good Fair ---- Good Good White-tailed deer Poor ---- ---- ---- ---- Small mammals Fair ---- ---- Fair Fair Small nongame birds Fair ---- ---- Fair Fair Upland game birds ---- ---- ---- Fair Poor Waterfowl ---- ---- ---- Poor Poor NUTRITIONAL VALUE : Fourwing saltbush is rated good in protein and energy value [7]. However, nutritional value is known to vary greatly by individual, accession, plant part, and phenological development. Crude protein levels range from 5.3 to 24.2 percent, with ash ranging from 13.3 to 16 percent [37,60]. Welch and Monsen [61] reported a mean winter crude protein value of 9.6 percent. Nutrient content of fourwing saltbush has been examined in detail [37,38,69]. The following values were obtained from a Utah site in November [37]: Crude Protein Crude Fiber Tannins Oxalates Carotene 10.4% 22.6% 5.8 mg/g 1.9% 31.1mg/100g Mineral content is as follows [38]: Ash P Fe K Ca Na (percent dry weight) 12.89 .23 .02 4.68 1.60 .18 In vitro digestibility of fourwing saltbush ranges from 29.1 to 46.9 percent or more, with an average value of 38.3 percent [61]. Wintering white-tailed or mule deer require approximately 50 percent digestibility, suggesting the need to mix fourwing saltbush with species such as big sagebrush, and dormant grasses to satisfy nutritional needs [61]. COVER VALUE : Fourwing saltbush has been planted to provide cover for upland game birds in many parts of California since the 1960's [46]. In shrub tests at a semiarid southern Idaho site, fourwing saltbush exhibited the highest mean cover index (derived from crown diameter, growth form, and leaf type and retention) for pheasant, California quail, and gray partridge [46]. However, growth form and leaf retention and thus cover value vary greatly by individual plant and accession. Cover value of fourwing saltbush has been rated as follows [7]: CO MT UT WY Pronghorns Poor ---- Fair Poor Elk ---- ---- Poor Poor Mule deer Poor ---- Fair Poor White-tailed deer ---- ---- ---- Poor Small mammals Fair Fair Good Poor Small non-game birds ---- Fair Fair Poor Upland game birds Fair Fair Fair Poor Waterfowl ---- ---- Poor Poor VALUE FOR REHABILITATION OF DISTURBED SITES : Fourwing saltbush has been widely used for rehabilitating mine spoils, roadsides, and oil well reserve pits high in soluble salts [41]. It is well suited for revegetating saline sites in southern and northern desert shrublands, pinyon-juniper woodlands, and mountain brush communities [72]. A number of cultivars have been developed including 'Rincon,' 'Wytana,' and 'Marana.' 'Rincon,' originally from north-central New Mexico, is adapted to much of the Intermountain region and grows well on sagebrush, pinyon-juniper woodland, and mountain brushland sites ranging from 3,000 to 7,600 feet (915-2,318 m) in elevation which receive 9 to 23 inches (23-58 cm) of precipitation annually [3]. It is characterized by extremely rapid growth and high productivity. 'Marana,' from southern California, is a hot desert cultivar which has been widely planted from southern Arizona to western Texas [53]. It does not survive temperatures below 10 degrees F (-12 degrees C). 'Wytana,' another widely used cultivar, originated from a fourwing saltbush-saltsage cross. It grows well on coal, uranium, bentonite, and hard rock mine spoils in Montana and Wyoming [3]. Researchers strongly recommend matching the cultivar or strain to be used to the site in which it is to be grown. Cold-tolerant cultivars may sometimes survive in warm climates, but hot desert cultivars often succumb during harsh cold winters [68]. Evidence from a California study suggests that rabbits and small rodents prefer strains from distant areas to those adapted to the site [35]. Nonadaptive plants may be seriously damaged or killed by these herbivores. Seed may be broadcast or drill-seeded, but broadcasting often produces better results [39]. However, seeding success is generally somewhat sporadic. Seeding specifications by habitat zones are as follows [39]: habitat broadcast (lbs/acre) drilled (lbs/acre) Big sagebrush 1 0.5 Big sagebrush-severely 2 2 disturbed Blackbrush 5 2.5 (Coleogyne ramossisima) Black greasewood 1-2 0.5-1 Inland saltgrass 4 2 (Distichlis stricta) Mountain brushland 1 0.5 Shadscale saltbush 1.5 1 (Atriplex confertifolia) Seedlings, which tend to be more drought tolerant and less susceptible to predation, may be transplanted with good results [46,72]. Seedlings are generally transplanted during the early spring, since 3 weeks or more of good soil moisture is required for establishment [9]. On coal-based acidic spoils, pH adjustment through the application of lime, and the addition of phosphorus may be necessary [45]. Sand or ash may be spread over the spoils, the sand top-dressed, and sand or shale incorporated into the spoils to improve fourwing saltbush growth [45]. Seedling survival is generally greater in areas lacking significant amounts of perennial grasses [4]. A number of studies have documented seedling success, relative costs, and growth rates on various types of mine sites in several western states [1,20,30,32]. Pertinent data are presented below. Wyoming- Seeding success and expenses at a Wyoming mine site were as follows [20]: Seeding rate Cost per acre Established seedlings Cost per per acre per 1,000 seeds seedling 1.0 lb $20.00 3.30 0.12 52,000 seeds First-year survival of bareroot transplants was estimated at 84 percent, with a cost per plant of $0.24 [20]. Nevada- On a seeded mine site in north-central Nevada, fourwing saltbush seedlings grew rapidly and matured within 4 years [30]. New Mexico- A New Mexico mine rehabilitation project was direct-seeded with fourwing saltbush without irrigation and drip-irrigated transplants. Growth here after 5 years was as follows [1]: Survival Height Crown Diameter Plot 1 62% 72.4 cm 55.4 cm Plot 2 88% 62.2 cm 59.7-98.3 cm Arizona- Fourwing saltbush successfully reestablished on southwestern Arizona copper mine spoils with the following soil characteristics [32]: pH Sol. salts Organics Na P NO3N (ppm) (%) (ppm) (ppm) (ppm) Tailing 7.75 355 .21 66 31 22 Overburden 7.85 2,452 .14 135 2 7 Mulching and irrigation are often required for establishment on mine spoils [59]. Seven years after planting, growth of fourwing saltbush was as follows [32]: Plant Height (m) Diameter of Cover (m) Tailing 1.4 2.6 Overburden 1.5 3.1 OTHER USES AND VALUES : Fourwing saltbush has been planted along many highways in the Southwest [46]. It has been used to stabilize roadsides and other disturbed areas and to improve production of depleted rangelands. It can be of great value in watershed rehabilitation by trapping sediments on alluvial floodplains [1]. MANAGEMENT CONSIDERATIONS : Grazing: Fourwing saltbush often increases in response to heavy grazing [65] and generally shows good recovery even when grazed fairly heavily during the spring and fall [44]. In an Idaho study, up to 50 percent utilization of annual growth by cattle did not adversely affect fourwing saltbush [44]. The amount of available forage typically increases throughout the growing season as follows [44]: 12 g/sq m May 33 g/sq m July 43 g/sq m August Livestock poisoning: Fourwing saltbush grown in selenium-enriched soil can accumulate selenium in excess of 160 p/m, creating a hazard to browsers using large amounts of the plant [5]. Dayton [6] noted that fourwing saltbush could sometimes poison sheep and if fed in concentration could possibly cause scours in cattle. Biomass: Fourwing saltbush herbage production has ranged from 5,195 to 5,379 pounds/acre (5,903-6,113 kg/ha) [37]. Herbage production could be increased to 6,679 to 8,949 pounds/acre (7,590-10,169 kg/ha) by closely spacing plants [37]. Productivity per plant ranges from 0.43 to 3.20 pounds (197-1,451 g) but averages approximately 1.49 pounds (664 g) [61]. The cultivar 'Rincon' can produce from 5.72 to 9.69 pounds per plant (2,600-4,400 g) [61]. Diploids tend to be more productive than tetraploids, although variation by individual and accession is common [37]. Interaction with grasses: The presence of fourwing saltbush enhances growth of grasses such as crested wheatgrass (Agropyron cristatum). A greater concentration of nitrogen and other minerals under the fourwing saltbush canopy may contribute to increased grass density [37,44].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Atriplex canescens | Fourwing Saltbush
GENERAL BOTANICAL CHARACTERISTICS : Fourwing saltbush is an erect, warm-season, freely branching evergreen shrub [44,69] which generally grows from 1 to 7 feet (30-200 cm) in height and from 1 to 15 feet (30-450 cm) in crown diameter [25]. A giant or gigas form which is found in the Little Sahara Sand Dunes near Jerico, Utah grows at nearly twice the rate of other fourwing saltbush populations and typically reaches 8 to 15 feet (244-457 cm) in height, with a crown spread of 12 to 15 feet (366-457 cm) [49,54]. Growth form of fourwing saltbush varies from open and treelike to a dense, closed canopy [47]. Fourwing saltbush is described as the most variable and rapidly evolving species in North America [53]. Populations and individuals exhibit great variation in chemical composition, reproduction, palatability, seed production, sex expression, growth form, winter hardiness, leaf retention, and tolerance to soil salinity or alkalinity [27]. Numerous varieties, races, ecotypes, and forms, each adapted to a specific habitat, have been identified. Diploid and polyploid races occur (2n, 4n, 6n, 10n, and 12n), with most populations autotetraploid (4n) [51,53]. Most chromosomal races are morphologically distinct enough to permit easy identification [51]. Most populations of fourwing saltbush include both dioecious and low frequencies of monoecious individuals [54]. Crowding, drought, and winter-induced stress can all result in sex changes, usually by the pistillate individuals which assume male characteristics [24,70]. Leaves are sessile to sub-sessile, entire, and gray-scrufy [69]. Some accessions produce summer leaves which are followed by winter leaves, whereas others produce only summer leaves [53]. Fourwing saltbush has a deep and extensive root system, which can extend to 19.5 feet (594 cm) in depth [6]. A plant 3.5 feet (107 cm) tall with a crown spread of 4 feet (121 cm) was found to have roots 6.5 feet (198 cm) deep in a 10-foot (304.8 cm) radius [34]. Fourwing saltbush accumulates wood annually [50]. Mature plants often have considerable amounts of dead wood in the crown (up to 60 percent of the total wood)[16]. Woody tissues apparently absorb water in the spring when moisure has evaporated [39]. Fruit of the fourwing saltbush is a wind- or gravity-dispersed, winged utricle [9]. Fruit size and production are highly variable. Leaves and fruit may persist into or even through the winter [39]. Fourwing saltbush is generally resistant to drought and tolerant of soil salinity and alkalinity [37]. Salts from the soil in which it grows tend to accumulate in the tissue of fourwing saltbush. These accumulated salts may act as an "antifreeze" in more northern climates or alternately may promote greater drought tolerance [50]. The lifespan of fourwing saltbush is variable. On neutral soils in mountain brushlands, maturation is rapid, with senecence occurring at approximately 10 years [39]. However, on drier alkaline sites, the lifespan of fourwing saltbush is significantly longer [39]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Seed: Fourwing saltbush typically produces an abundance of light, wind- or gravity-dispersed seed [9]. Seed production in this prolific species has been observed in plants as young as 1 year of age, although this is probably uncommon [9]. Wide annual fluctuation in annual seed production occurs as does ecotypic variability in the amount of seed produced at a particular site [9,26]. Seed fill is also highly variable, ranging from very little to 75 percent or more [9]. Cultivars generally produce fill in excess of 70 percent [9]. Little is known about length of seed viability under natural conditions; however, seeds have remained viable for 10 to 16 years in laboratory tests [40,46]. Seeds often remain on the plants until the following spring and can persist on the plant for up to 2 years in some instances [9]. Germination: Germination is often erratic and varies greatly according to ecotype, race, or form [41]. Germination rates are generally higher in diploid than in tetraploid chromosomal races [55]. These differences are illustrated below [54]: Pollen Seed Seed Germination Fertility Germination Fill of Filled Seed (%) # % # % # % Diploids 72 316/1100 28.7 1194/3720 32 1053/1194 88.11 Tetraploids 51 549/5800 9.5 1400/4093 34 140/2828 4.90 Maximum germination occurs between 55 and 75 degrees F (13-24 degrees C) [67]. Germinating fourwing saltbush is best able to tolerate moisture stress at 63 degrees F (17 degrees C) [41] and does not respond to the presence or absence of light [46]. Dewinging seeds and using a hammermill generally speed germination [41]. A 10-month afterripening period typically enhances germination of fourwing saltbush [9]. Chemical treatments, scarification, and water soaks have been tried, but none of these methods have consistently improved germination [9]. The removal of pericarps generally speeds germination [58] but seed coats are quite variable. Scarification has increased germination in some types of fourwing saltbush seed but has had little effect on others [67]. Although timing varies greatly, seedlings can emerge in only 6 to 20 days [9]. Seed Source Temperature Days % Germination CA 65-75 degrees F 30 44 NM 65 degrees F 30 94 UT 32-38 degrees F 50 53 Vegetative regeneration: The fourwing saltbush is known to reproduce vegetatively through root sprouting or layering. Adventitious buds sometimes form on the root crown or underground portions of the stem [63]. The relative importance of vegetative reproduction is not well documented for this species. However, a study of two New Mexico sites revealed that up to 77 percent and 96 percent of the plants respectively were of root sucker origin [63]. The gigas diploid form which grows in the Little Sahara Sand Dunes of Utah is known to layer [25]. SITE CHARACTERISTICS : Fourwing saltbush is well adapted to a wide range of temperature and soil conditions. It is highly tolerant of drought, salinity, and alkalinity. Fourwing saltbush occurs on sand dunes, in gravelly washes, on mesas, ridges, alluvial plains, and slopes [25]. Soils: Fourwing saltbush is particularly common on deep, well-drained, sandy often alkaline soils in desert and foothill ranges of the Great Basin [49]. However, it also grows well on heavy clay and on selenium-enriched soil [5,25]. Although fourwing saltbush has been reported on sites with as much as 1 percent soluble salts [39], soil salinity usually ranges from 307 to 1,693 p/m, and healthy plants have been observed growing on soils with soluble salts in excess of 4,229 p/m [60]. Cultivars have been developed which grow readily on coal, uranium, bentonite, and copper or other hard rock mine spoils [3]. Elevation: Generalized elevational ranges are as follows [7]: from 3,900 to 8,600 feet (1,190 to 2,623 m) in CO 4,200 to 8,000 feet (1,281 to 2,440 m) in UT 4,400 to 6,900 feet (1,342 to 2,105 m) in WY SUCCESSIONAL STATUS : Facultative Seral Species Fourwing saltbush occurs in a number of climax saltbush-grassland communities. It also readily colonizes newly disturbed areas and is well represented in many early seral communities [62]. SEASONAL DEVELOPMENT : Leaves generally remain succulent even during midsummer [29] when most annual growth has ceased [44]. Depending on the accession or even the individual, leaves may be retained throughout the winter months. Some accessions produce summer leaves followed by winter leaves, whereas others produce only summer leaves [53]. In the Upper Sonoran Desert, growth resumes in spring to early summer, and in the Lower Sonoran Desert, renewal growth begins with summer rains [59]. Time of flowering is as follows [7]: Beginning of Flowering End of Flowering CO May September MT August October ND July August UT May September WY June September Fruit generally ripens from October to December, with seed dispersal from October through April (3 to 4 months after flowering) [9,59]. In some instances, seed may remain on the plants for 1 or 2 years [9].

FIRE ECOLOGY

SPECIES: Atriplex canescens | Fourwing Saltbush
FIRE ECOLOGY OR ADAPTATIONS : Fourwing saltbush is a fire-tolerant sprouter which typically recovers fully within 2 or 3 years after a burn [64]. Because of its unusually low volatilization rate, fourwing saltbush has been described as "fire resistant" [38]. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud root crown Initial-offsite colonizer (off-site, initial community)

FIRE EFFECTS

SPECIES: Atriplex canescens | Fourwing Saltbush
IMMEDIATE FIRE EFFECT ON PLANT : Fourwing saltbush is reportedly tolerant of fire. It is characterized by a low volatization rate which renders the plant relatively "fire-resistant" [38]. Char formation is increased at the expense of flammable volatile compounds [38]. In most locations, underground regenerative structures survive even when aboveground portions of the plant are consumed by fire [64]. However, in southern Idaho, forwing saltbush seedlings were readily killed by fire [S. Whisenant, pers. comm. 1987]. Young plants may be more susceptible to fire-induced mortality, or ecotypic variation in susceptibility may exist [S. Whisenant, pers. comm. 1987]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Fourwing saltbush generally sprouts vigorously from the root crown or underground portions of the stem following fire [64]. However, no sprouting was observed after young plants were burned in southern Idaho [S. Whisenant, pers. comm. 1987]. Plants are presumably capable of reestablishing some sites through an abundance of wind-dispersed seed from adjacent unburned areas. Reestablishment is usually rapid, with full recovery possible within 2 or 3 years [64]. The cultivar 'Rincon' was seeded and successfully established within 2 years after fire in central Utah [4]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Fuels and flammability: Because of its unusually low volatilization rate, fourwing saltbush was tested for use as a firebreak species in southern California [38]. Researchers learned that fourwing saltbush communities usually average less than 15 tons of fuel per acre [33]. Research also indicated that the greater the ash content, the higher the moisture content of the foliage of fourwing saltbush [33]. Ash levels typically range from 5.6 to 24.2 percent [60]. Heat value of fourwing saltbush ranges from 7,500 to 10,000 BTUs per pound, with foliage averaging 8,475 BTUs per pound [33]. Postfire rehabilitation: Managers have successfully planted cultivars of fourwing saltbush on many burned sites with good results. Fourwing saltbush recovers rapidly and cultivars such as 'Rincon' have reestablished certain burned sites which had few competing perennial grasses within only 2 years after fire [4]. In postburn communities this shrub produced an average of 20 times the crown volume of winterfat and 40 times the crown volume of big sagebrush [4].

REFERENCES

SPECIES: Atriplex canescens | Fourwing Saltbush
REFERENCES : 1. Aldon, Earl F. 1984. Methods for establishing fourwing saltbush (Atriplex canescens [Pursh] Nutt.) on disturbed sites in the Southwest. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 265-268. [8029] 2. 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] 3. Carlson, Jack. 1984. Atriplex cultivar development. In: Proceedings-symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 176-182. [603] 4. Clary, Warren P.; Tiedemann, Arthur R. 1984. Development of `Rincon' fourwing saltbush, winterfat, and other shrubs from seed following fire. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 273-280. [646] 5. Davis, A. M. 1972. Selenium accumulation in a collection of Atriplex species. Agronomy Journal. 64: 823-824. [751] 6. Dayton, William A. 1931. Important western browse plants. Misc. Publ. 101. Washington, DC: U.S. Department of Agriculture. 214 p. [768] 7. 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] 8. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 9. Foiles, Marvin W. 1974. Atriplex L. saltbush. In: Schopmeyer, C. S., technical coordinator. Seeds of wood plants in the United States. Agric. Handb. 450. Washington, DC: U.S. Department of Agriculture, Forest Service: 240-243. [933] 10. 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] 11. Francis, Richard E.; Aldon, Earl F. 1983. Preliminary habitat types of a semiarid grassland. In: Moir, W. H.; Hendzel, Leonard, tech. coords. Proceedings of the workshop on Southwestern habitat types; 1983 April 6-8; Albuquerque, NM. Albuquerque, NM: U.S. Department of Agriculture, Forest Service, Southwestern Region: 62-66. [956] 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. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 14. Hodgkinson, Harmon S. 1987. Relationship of saltbush species to soil chemical properties. Journal of Range Management. 40(1): 23-26. [1175] 15. Holmgren, Arthur H.; Reveal, James L. 1966. Checklist of the vascular plants of the Intermountain Region. Res. Pap. INT-32. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 160 p. [1184] 16. Holmgren, Ralph C.; Brewster, Sam F., Jr. 1972. Distribution of organic matter reserve in a desert shrub community. Research Paper INT-130. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 15 p. [1187] 17. Johnston, Barry C. 1987. Plant associations of Region Two: Potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas. 4th ed. R2-ECOL-87-2. Lakewood, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Region. 429 p. [3519] 18. 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] 19. 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] 20. Luke, Forrest; Monsen, Stephen B. 1984. Methods and costs for establishing shrubs on mined lands in southwestern Wyoming. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 286-291. [1485] 21. 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] 22. Malcolm, C. V. 1972. Establishing shrubs in saline environments. In: McKell, Cyrus M.; Blaisdell, James P.; Goodin, Joe R., tech. eds. Wildland shrubs--their biology and utilization: An international symposium; Proceedings; 1971 July; Logan, UT. Gen. Tech. Rep. INT-1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 392-403. [1517] 23. McArthur, E. Durant; Blauer, A. Clyde; Noller, Gary L. 1984. Propagation of fourwing saltbush by stem cuttings. In: Tiedemann, Arthur R. [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. G. T. R. INT- 172. Ogden, UT: USDA, Forest Service, Intrmnt Forest & Range Ex. Sta.: 261-264. [1570] 24. McArthur, E. Durant; Freeman, D. C. 1982. Sex expression in Atriplex canescens: genetics and environment. Botanical Gazette. 143(4): 476-482. [1572] 25. McArthur, E. Durant; Plummer, A. Perry; Davis, James N. 1978. Rehabilitation of game range in the salt desert. In: Johnson, Kendall L., ed. Wyoming shrublands: Proceedings of the 7th Wyomingshrub ecology workshop; 1978 May 31-June 1; Rock Springs, WY. Laramie, WY: University of Wyoming, Range Management Division, Wyoming Shrub Ecology Workshop: 23-50. [1575] 26. McArthur, E. Durant; Sanderson, Stewart C. 1984. Distribution, systematics and evolution of Chenopodiaceae: an overview. In: Tiedemann, Arthur R. [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT:U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 14-24. [1577] 27. McArthur, E. Durant; Stevens, Richard; Blauer, A. Clyde. 1983. Growth performance comparisons among 18 accessions of fourwing saltbush (Atriplex canescens) at two sites in central Utah. Journal of Range Management. 36(1): 78-81. [1583] 28. Moir, W. H. 1983. A series vegetation classification for Region 3. In: Moir, W. H.; Hendzel, Leonard, tech. coords. Proceedings of the workshop on Southwestern habitat types; 1983 April 6-8; Albuquerque, NM. Albuquerque, NM: U.S. Department of Agriculture, Forest Service, Southwestern Region: 91-95. [1672] 29. Monsen, Stephen B.; Christensen, Donald R. 1975. Woody plants for rehabilitating rangelands in the Intermountain Region. In: Stutz, Howard C., ed. Wildland shrubs: Proceedings--symposium and workshop; 1975 November 5-7; Provo, UT. Provo, UT: Brigham Young Univeristy: 72-119. [1680] 30. Monsen, Stephen B.; Richardson, Bland Z. 1984. Seeding shrubs with herbs on a semiarid mine site with and without topsoil. In: Tiedemann, Arthur R. [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT:U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 298-305. [1683] 31. Noller, Gary L.; Stranathan, Sam E.; McArthur, E. Durant. 1984. Establishment and initial results from a `Rincon' fourwing saltbush seed orchard. In: Tiedemann, Arthur R. [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 196-204. [1770] 32. Norem, M. A.; Day, A. D.; Ludeke, K. L. 1982. An evaluation of shrub and tree species used for revegetating copper mine wastes in the south-western United States. Journal of Arid Environments. 5: 99-304. [1776] 33. Nord, Eamor C.; Countryman, Clive M. 1972. Fire relations. In: McKell, Cyrus M.; Blaisdell, James P.; Goodin, Joe R., eds. Wildland shrubs--their biology and utilization: Proceedings of the symposium; 1971 July; Logan, UT. Gen. Tech. Rep. INT-1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 88-97. [1773] 34. Nord, Eamor C.; Hartless, Patrick F.; Nettleton, W. Dennis. 1971. Effects of several factors on saltbush establishment in California. Journal of Range Management. 24(3): 216-223. [1774] 35. Nord, Eamor C.; Stallings, J. Russell. 1975. Rabbits show different preferenes according to saltbush ( Atriplex) species and strains. In: Stutz, Howard C., ed. Wildland shrubs: Proceedings-- symposium and workshop: 1975 November 5-7; Provo, UT. Provo, UT: Brigham Young University: 147-148. [1775] 36. Northington, D. K.; Goodin, J. R. 1975. Variability in natural populations of Atriplex canescens. In: Stutz, Howard C., ed. Wildland shrubs: Proceedings-- symposium and workshop; 1975 November 5-7; Provo, UT. Provo, UT: Brigham Young University: 149. [1780] 37. Ostyina, R. M.; McKell, C. M.; Malecheck, J. M.; Van Epps, G. A. 1984. Potential of Atriplex and other chenopod shrubs for increasing range productivity and fall and winter grazing. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 215-219. [1805] 38. Philpot, C. W. 1970. Influence of mineral content on the pyrolysis of plant materials. Forest Science. 16(4): 461-471. [1883] 39. Plummer, A. Perry; Christensen, Donald R.; Monsen, Stephen B. 1968. Restoring big-game range in Utah. Publ. No. 68-3. Ephraim, UT: Utah Division of Fish and Game. 183 p. [4554] 40. Plummer, Mark. 1984. Considerations in selecting chenopod species for range seeding. In: Tiedemann, Arthur R. [and others], compilers. Proceedings--symposium on thebiology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 183-186. [1903] 41. Potter, R. L.; Ueckert, D. N.; Petersen, J. L.; McFarland, M. I. 1986. Germination of fourwing saltbush seeds: interaction of temperature, osmotic potential, and pH. Journal of Range Management. 39(1): 43-46. [1909] 42. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 43. Richardson, Steven G.; Barker, Jerry R.; Crofts, Kent A.; Van Epps, Gordon A. 1979. Factors affecting root of stem cuttings of salt desert shrubs. Journal of Range Management. 32(4): 280-283. [1975] 44. Rumbaugh, M. D.; Johnson, D. A.; Van Epps, G. A. 1982. Forage yield and quality in a Great Basin shrub, grass, and legume pasture experiment. Journal of Range Management. 35(5): 604-609. [2042] 45. Scholl, D. G.; Miyamoto, S. 1983. Response of alkali sacaton and fourwing saltbush to various amendments on coal mine spoils from northwestern New Mexico. Reclamation and Revegetation Research. 2: 227-236. [2085] 46. Shaw, Nancy; Monsen, Stephen B. 1984. Nursery propagation and outplanting of bareroot Chenopod seedlings. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 251-260. [2123] 47. Shaw, Nancy; Sands, Alan; Turnipseed, Dale. 1984. Potential use of fourwing saltbush and other dryland shrubs for upland game bird cover in southern Idaho. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 206-214. [2125] 48. Stubbendieck, J.; Hatch, Stephan L.; Hirsch, Kathie J. 1986. North American range plants. 3rd ed. Lincoln, NE: University of Nebraska Press. 465 p. [2270] 49. Stutz, Howard C. 1972. Genetic improvement in crop species as contrasted with possibilities in shrubs. In: McKell, Cyrus M.; Blaisdell, James P.; Goodin, Joe R., eds. Wildland shrubs--their biology and utilization: An international symposium: Proceedings; 1971 July; Logan, UT. Gen. Tech. Rep. INT-1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 139-150. [2278] 50. Stutz, Howard C. 1978. Explosive evolution of perennial Atriplex in western North America. Great Basin Naturalist Memoirs. 2: 161-168. [2279] 51. Stutz, Howard C. 1979. Navajo mine project. In: Land reclamation program annual report 1978. Argonne, IL: Argonne National Laboratory: 30-37. [2281] 52. Stutz, Howard C. 1984. Atriplex hybridization in western North America. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 25-27. [2284] 53. Stutz, Howard C.; Carlson, J.R. 1985. Genetic improvement of saltbush (Atriplex) and other chenopods. In: Carlson, Jack R.; McArthur, E. Durant, chairmen. Range plant improvement in western North America: Proceedings of a symposium at the annual meeting of the Society for Range Management; 1985 February 14; Salt Lake City, UT. Denver, CO: Society for Range Management: 89-92. [2287] 54. Stutz, Howard C.; Melby, James M.; Livingston, Gordon K. 1975. Evolutionary studies of Atriplex: a relic gigas diploid population pf Atriplex canescens. American Journal of Botany. 62(3): 236-245. [2288] 55. Stutz, Howard C.; Pope, C. Lorenzo; Leslie, Thomas. 1975. Germination studies in Atriplex. In: Stutz, Howard C., ed. Wildland Shrubs: Proceedings-- symposium and workshop: 1975 November 5-7; Provo, UT. Provo, UT: Brigham Young University: 150. [2289] 56. Turner, Raymond M. 1982. Great Basin desertscrub. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 145-155. [2373] 57. Van Dyke, Walter A.; Sands, Alan; Yoakum, Jim; [and others]. 1983. Wildlife habitats in managed rangelands--the Great Basin of southeastern Oregon: bighorn sheep. Gen. Tech. Rep. PNW-159. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest and Range Experiment Station. 37 p. [2417] 58. Warren, Daniel C.; Kay, Burgess L. 1984. Pericarp inhibition of germination of Atriplex confertifolia. In: Tiedemann, Arthur R. [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT:U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 168-174. [2457] 59. Wasser, Clinton H. 1982. Ecology and culture of selected species useful in revegetating disturbed lands in the West. FWS/OBS-82/56. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service. 347 p. [4837] 60. Welch, Bruce L. 1978. Relationship of soil salinity, ash, and crude protein in Atriplex canescens. Journal of Range Management. 31(2): 132-133. [2478] 61. Welch, Bruce L.; Monsen, Stephen B. 1981. Winter crude protein among accessions of fourwing saltbush grown in a uniform garden. Great Basin Naturalist. 41(3): 343-346; 1981. [2487] 62. Wilkins, Scott D.; Klopatek, Jeffrey M. 1984. Moisture stress, Atriplex species, and reclamation. In: Tiedemann, Arthur R. [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT:U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 97-107. [2563] 63. Woodmansee, Robert G.; Potter, Loren D. 1970. Vegetative reproduction of fourwing saltbush in New Mexico. Journal of Range Management. 23: 371. [2598] 64. Wright, Henry A. 1980. The role and use of fire in the semidesert grass-shrub type. Gen. Tech. Rep. INT-85. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 24 p. [2616] 65. Yensen, Dana L.; Smith, Graham W. 1984. Big sagebrush-winterfat and big sagebrush-Nuttall saltbush mosaic vegetation in southwestern Idaho. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 28-33. [2635] 66. Young, James A.; Evans, Raymond A.; Roundy, Bruce A.; Cluff, Greg J. 1984. Ecology of seed germination in representative Chenopodiaceae. In: Tiedemann, Arthur R. [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 159-165. [2675] 67. Young, James A.; Kay, Burgess L.; Evans, Raymond A. 1984. Winter hardiness and jackrabbit preference in a hybrid population of fourwing saltbush (Atriplex canescens). In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard, C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 59-65. [2679] 68. Van Epps, G.A. 1975. Winter injury to fourwing saltbush. Journal of Range Management. 28(2): 157-159. [2420] 69. Wallace, A.; Romney, E. M. 1972. Radioecology and ecophysiology of desert plants at the Nevada Test Site. Rep. TID-25954. [Washington, DC]: U.S. Atomic Energy Commission, Office of Information Services. 439 p. [15000] 70. Clark, Richard A. 1983. The influence of environmental stress on male and female functions in two dioecious shrubs of Utah. Provo, UT: Brigham Young University; 1983. 30 p. Manuscript of a journal article in partial fulfillment of the requirments for M.S. degree. [631] 71. Smith, Arthur D.; Beale, Donald M. 1980. Pronghorn antelope in Utah: some research and observations. Publication No. 80-13. Salt Lake City, UT: Utah Division of Wildlife Resources. 88 p. [5305] 72. Plummer, A. Perry. 1977. Revegetation of disturbed Intermountain area sites. In: Thames, J. C., ed. Reclamation and use of disturbed lands of the Southwest. Tucson, AZ: University of Arizona Press: 302-337. [171] 73. 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] 74. 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]

Index

Related categories for Species: Atriplex canescens | Fourwing Saltbush

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