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Introductory

SPECIES: Artemisia cana ssp. bolanderi | Bolander Silver Sagebrush
ABBREVIATION : ARTCANB SYNONYMS : Artemisia bolanderi Gray Artemisia tridentata Nutt. ssp. bolanderi (Gray) Hall & Clements Artemisia tridentata var. bolanderi (Gray) McMinn SCS PLANT CODE : ARCAB3 COMMON NAMES : Bolander silver sagebrush Bolander sagebrush white sagebrush silver sagebrush TAXONOMY : The fully documented scientific name for Bolander silver sagebrush is Artemisia cana ssp. bolanderi (Gray) Ward. The taxonomy presented here follows that of Beetle [1], who differentiated three subspecies of silver sagebrush based on morphological, geographical, and ecological characteristics. Silver sagebrush occurs in both diploid and tetraploid forms [17,38]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : N. McMurray, September 1986 LAST REVISED BY AND DATE : N. McMurray, December 1988 AUTHORSHIP AND CITATION : McMurray, Nancy E. 1986. Artemisia cana ssp. bolanderi. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Artemisia cana ssp. bolanderi | Bolander Silver Sagebrush
GENERAL DISTRIBUTION : Bolander silver sagebrush has the most western distribution and most restricted range of the three silver sagebrush subspecies. It occurs primarily in the central basins of Oregon south through the Great Basin areas of eastern California and extreme western Nevada [1,4,26,35]. An isolated population has been described in the San Bernardino Mountains of California [1]. Bolander silver sagebrush has also been recorded in western Idaho [35]. ECOSYSTEMS : FRES21 Ponderosa pine FRES29 Sagebrush FRES30 Desert shrub FRES35 Pinyon - juniper STATES : CA ID NV OR ADMINISTRATIVE UNITS : NO-ENTRY BLM PHYSIOGRAPHIC REGIONS : 4 Sierra Mountains 5 Columbia Plateau 6 Upper Basin and Range 8 Northern Rocky Mountains KUCHLER PLANT ASSOCIATIONS : K010 Ponderosa shrub forest K023 Juniper - pinyon woodland K024 Juniper - steppe woodland K038 Great Basin sagebrush K040 Saltbush - greasewood K055 Sagebrush steppe SAF COVER TYPES : 237 Interior ponderosa pine 238 Western juniper SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Mature stands of Bolander silver sagebrush are indicative of climax conditions within nonforested communities. Little identification of habitat types has been done for communities occupied by this subspecies. A Bolander silver sagebrush/mat muhly (A. cana ssp. bolanderi/ Muhlenbergia richardsonis) habitat type has been described for Idaho [10]. These sites generally have a sparse understory dominated by mat muhly and Baltic rush (Juncus balticus). Apparently similar sites in Oregon are characterized by a Nevada bluegrass (Poa nevadensis) understory. A silver sagebrush community has also been described for upland sites surrounding seasonal ponds in California [36]. Bottlebrush squirreltail (Elymus elymoides) was the herbaceous dominant on these sites.

VALUE AND USE

SPECIES: Artemisia cana ssp. bolanderi | Bolander Silver Sagebrush
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Bolander silver sagebrush basins are unique habitats that add to diversity and increase edge in areas dominated by low and tall sagebrush species. These sites are important foraging areas for mule deer, pronghorn, and sage grouse [4]. In Oregon, Bolander silver sagebrush is a highly preferred mule deer winter browse [24]. Mule deer use Bolander silver sagebrush communities more often than expected given their availability on central Oregon winter ranges [414]. Although browse use declines throughout the spring and summer, deer heavily utilize associated forage plants that are created by spring flooding, particularly Newberry cinquefoil (Potentilla newberryi) and desert combleaf (Polyctenium fremontii) [14]. Throughout the summer these "flats" are frequently used by pronghorn as resting and bedding areas. Generally, livestock utilization of Bolander silver sagebrush basins is slight; in most cases the herbaceous understory is not maintained through the grazing season. PALATABILITY : Bolander silver sagebrush is a highly palatable forage species on mule deer winter ranges in Oregon [14]. In feeding trials with captive animals this subspecies was among the more highly preferred of the seven sagebrush taxa compared [24]. It was highly preferred by mule deer in both the fall and winter and was utilized but not preferred by domestic sheep. NUTRITIONAL VALUE : The silver sagebrush complex is rated as fair in energy value and fair to good in protein value [5]. COVER VALUE : Cover is typically sparse in alkaline basins dominated by Bolander silver sagebrush. Not only do stands occupy sites of low productive potential [11], but many have been seriously overgrazed. Plants are seldom tall enough or dense enough to provide cover for animals larger than geese, swans, coyotes, or rabbits [4]. VALUE FOR REHABILITATION OF DISTURBED SITES : Bolander silver sagebrush appears to be a good revegetation candidate on sites to which it is adpated. Not only do plants sprout and layer, but they are also able to tolerate wide fluctuations in soil moisture conditions. However, no information was located regarding its use in rehabilitation projects. Plains silver sagebrush (A. cana ssp. cana) has been successfully established on coal spoils in eastern Montana [9]. McArthur [16] indicated that Bolander silver sagebrush is generally adapted for planting on sites having poorly drained, heavy soils. Monsen [19] recommended that silver sagebrush be used for riparian plantings in mountain brush and sagebrush/desert communities. Plants can be propagated via stem or root cuttings and also by wildlings [6,9]. Transplant material should consist of rooted cuttings, 1-0 nursery stock, or hardened-off, containerized stock. OTHER USES AND VALUES : Waterholes are often developed in basins dominated by Bolander silver sagebrush. Drainage ditches are dug across the basin floor to rapidly concentrate spring-runoff from wide, shallow naturally occurring ponds into deeper reserviors where the water does not evaporate as readily. Consequently, a reliable water source is maintained further into the livestock grazing season [14]. In smaller basins the drainage is so greatly improved that big sagebrush (Artemisia tridentata) and rabbitbrush (Chrysothamnus ssp.) are able to invade and sometimes replace stands of silver sagebrush [4,14]. Another method of creating additional water sources without sacrificing the unique qualities of silver sagebrush communities involves the installation of "guzzlers" (catchment aprons with storage tanks) in adjacent community types [14]. Silver sagebrush has been used as an ornamental in England. In America, this species has been used historically as fuelwood by both Indians and white settlers [17]. MANAGEMENT CONSIDERATIONS : Opportunities to increase forage production within Bolander silver sagebrush basins are low. Few introduced species are adapted to the heavy clay soils and seasonal flooding characteristic of these sites [3]. Stands are best left untilled and unsprayed.

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Artemisia cana ssp. bolanderi | Bolander Silver Sagebrush
GENERAL BOTANICAL CHARACTERISTICS : Bolander silver sagebrush is an erect or spreading, thickly branched, long-lived, evergreen shrub usually 12 to 24 inches (30 to 60 cm) tall [1,30,35]. This species is both highly drought resistant and also able to tolerate temporary flooding [4,11,31]. Bolander silver sagebrush is the shortest of the three subspecies of silver sagebrush. Branching patterns produce crowns that are somewhat irregularly shaped. Although leaf morphology is highly variable, leaves are generally tapered at both ends, unlobed, and candescent. This subspecies is morphologically quite similar to mountain silver sagebrush except for its characteristic dense stem tomentum [26]. Although allelopathy has been documented in plains silver sagebrush [9], its occurrence in this subspecies has not been verified. Plants of the silver sagebrush complex typically produce a shallow to deep, well-branched root system [31]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Bolander silver sagebrush is generally thought to employ both sexual and vegetative modes of reproduction. Within the Artemisia genus, the silver sagebrush complex is distinguished by its ability to resprout following disturbance; however, resprouting abilities vary between the three subspecies [37]. Bolander silver sagebrush plants can sprout from the root crown and also readily layers [1,4]. Vegetative regeneration would appear to be important on sites subjected to annual spring flooding. Reporting on the results of rangeland revegetation projects along the east slope of the Sierra Nevada, Cornelius and Talbot [3] found that mechanical control of Bolander silver sagebrush was most effective when soils were plowed to depths of 6 to 8 inches (15 to 20 cm). Severing plants several inches (approximately 5 cm) below the soil surface or mowing caused crown sprouting in the majority of plants [3]. The role of seedling establishment remains unclear within the ecology of this subspecies. Sagebrush reestablishment occurred via the growth of new or resprouted individuals on sites in Oregon where plants were top-killed following prolonged spring flooding [4]. A number of studies have reported on regeneration of plains silver sagebrush. See Artemisia cana ssp. cana regeneration slot for details. SITE CHARACTERISTICS : Bolander silver sagebrush is restricted to internally drained, alkaline basins scattered along the western edge of the sagebrush-grass region at elevations ranging from 3,500 to 6,000 feet (1,067-1,830 m) [4,11,35]. Mean annual precipitation on these semiarid sites ranges from 8 to 10 inches (20-25 cm) [31]. In Oregon, plants apparently grade into mountain silver sagebrush at elevations above 5,500 feet (1,677 m). The silver sagebrush complex is unique among the Artemisia genus in its ability to tolerate soil saturation and seasonal flooding. Bolander silver sagebrush is typically associated with sites that have standing water for at least a month in the late winter or early spring; water depths may reach 1 to 2 feet (0.3-0.6 m). Occassionally the persistence of standing water extends beyond the limits of this subspecies, and plants die back to the root. Resprouts and new individuals, however, are able to regain coverages within approximately 3 years [4]. Most soils are extremely clayey and are often derived from granite [26,35]. Summer drying produces wide, deep cracks in these clay soils into which flaking surface layers readily slough [3]. This subspecies typically occupies the relatively level terrain of alkaline basins, but stands occasionally occur on cold, wet slopes between 7,000 and 8,000 feet (2,134 and 2,440 m) in California [3]. Historically, vegetal cover has been sparse in basins dominated by Bolander sagebrush. Winward [35] suggests that this condition is more a function of soil chemistry than an evidence of past abuse. Seasonal flooding of sites basically eliminates most plants common to sagebrush-steppe communities. Bolander sagebrush is typically the only shrub present, and shrub interspaces remain essentially barren. Moist spring conditions create a lush herbaceous undergrowth; these plants, however, are not maintained through the livestock grazing season. Species adapted to such extremes of flooding and drying include mat muly (Muhlenburgia richardsonis), spike rush (Eleocharis spp.), wire rush (Juncus spp.), Baltic rush (Juncus balticus), Douglas sedge (Carex douglasii), Newberry cinquefoil, showy downingia (Downingia elegans), desert combleaf, tiny mousetail (Myosurus minimus), bottlebrush squirreltail (Elymus elymoides), and cheatgrass (Bromus tectorum) [4]. SUCCESSIONAL STATUS : Mature, self-perpetuating stands of Bolander silver sagebrush are indicative of climax conditions. Plants are established during early seral stages and coexist with later arriving species. Apparently, management activities which improve drainage on Bolander silver sagebrush sites result in stands being invaded and in some instances replaced by big sagebrush and rabbitbrush [3]. SEASONAL DEVELOPMENT : Phenological development of Bolander silver sagebrush is not well documented. The following generalized sequence has been described by Beetle [1]: Immature flower heads early August Flowering late August or early September Seeds ripe October

FIRE ECOLOGY

SPECIES: Artemisia cana ssp. bolanderi | Bolander Silver Sagebrush
FIRE ECOLOGY OR ADAPTATIONS : Bolander silver sagebrush resprouts vigorously from the crown and rhizomes following most fires. Postfire regeneration also involves the germination of wind-dispersed seed [28,348,10]. In most cases, recovery is relatively rapid. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud root crown Rhizomatous shrub, rhizome in soil Initial-offsite colonizer (off-site, initial community)

FIRE EFFECTS

SPECIES: Artemisia cana ssp. bolanderi | Bolander Silver Sagebrush
IMMEDIATE FIRE EFFECT ON PLANT : Little fire effects information is available for Bolander silver sagebrush; plants are probably top-killed by most fires. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Bolander silver sagebrush regenerates via root sprouting and wind-dispersed seed following disturbance. Specific fire response information for this subspecies is lacking; fire response information on the silver sagebrush complex as a whole indicates that densities are rapidly regained and even enhanced following burning. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : The ability of Bolander silver sagebrush stands to carry fire is low because of seasonally high water tables and sparse understories. Plant manipulation via prescribed burning in communities dominated by this subspecies appears questionable since few species are adapted to the moisture regimes and alkaline soils characterized by these sites [4,32].

REFERENCES

SPECIES: Artemisia cana ssp. bolanderi | Bolander Silver Sagebrush
REFERENCES : 1. Beetle, A. A. 1960. A study of sagebrush: The section Tridentatae of Artemisia. Bulletin 368. Laramie, WY: University of Wyoming, Agricultural Experiment Station. 83 p. [416] 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. Cornelius, Donald R.; Talbot, M. W. 1955. Rangeland improvement through seeding and weed control on east slope Sierra Nevada and on southern Cascade Mountains. Agric. Handb. 88. Washington, DC: U.S. Department of Agriculture, Forest Service. 51 p. [7510] 4. Dealy, J. Edward; Leckenby, Donavin A.; Concannon, Diane M. 1981. Wildlife habitats on managed rangelands--the Great Basin of southeastern Oregon: plant communities and their importance to wildlife. Gen. Tech. Rep. PNW-120. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest and Range Experiment Station. 66 p. [786] 5. 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] 6. Everett, Richard L.; Meeuwig, Richard O.; Robertson, Joseph H. 1978. Propagation of Nevada shrubs by stem cutting. Journal of Range Management. 31(6): 426-429. [894] 7. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 8. 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] 9. Harvey, Stephen John. 1981. Life history and reproductive strategies in Artemisia. Bozeman, MT: Montana State University. 132 p. M.S. thesis. [1102] 10. Hironaka, M.; Fosberg, M. A.; Winward, A. H. 1983. Sagebrush-grass habitat types of southern Idaho. Bulletin Number 35. Moscow, ID: University of Idaho, Forest, Wildlife and Range Experiment Station. 44 p. [1152] 11. Johnson, Kendall L. 1987. Sagebrush types as ecological indicators to integrated pest management (IPM) in the sagebrush ecosystem of western North America. In: Onsager, Jerome A., ed. Integrated pest management on rangeland: State of the art in the sagebrush ecosystem. ARS-50. Washington, DC: U.S. Department of Agriculture, Agricultural Research Service: 1-10. [2841] 12. 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] 13. Leckenby, Donavin A. 1978. Mule deer occupancy of plant communities on a south-central Oregon winter range. Job Final Rep. Res. Proj. Seg. W-70-R. Portland, OR: Oregon Department of Fish and Wildlife. 78 p. [12496] 14. Leckenby, Donavin A.; Sheehy, Dennis P.; Nellis, Carl H.; [and others]. 1982. Wildlife habitats in managed rangelands--the Great Basin of southeastern Oregon: mule deer. Gen. Tech. Rep. PNW-139. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 40 p. [1432] 15. 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] 16. McArthur, E. Durant. 1983. Important shrubs for wildland plantings, Compositae ( Asteraceae). In: Monsen, Stephen B.; Shaw, Nancy, comp. Managing Intermountain rangelands-- improvement of range and wildlife habitats: Proceedings of symposia; 1981 September 15-17; Twin Falls, ID; 1982 June 22-24; Elko, NV. Gen. Tech. Rep. INT-157. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 150-157. [1567] 17. McArthur, E. Durant; Blauer, A. Clyde; Plummer, A. Perry; Stevens, Richard. 1979. Characteristics and hybridization of important Intermountain shrubs. III. Sunflower family. Res. Pap. INT-220. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 82 p. [1571] 18. McArthur, E. Durant; Stevens, Richard. 1986. Composite shrubs. Unpublished manuscript on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Labortory, Missoula, MT. 155 p. [7342] 19. Monsen, Stephen B. 1983. Plants for revegetation of riparian sites within the Intermountain region. In: Monsen, Stephen B.; Shaw, Nancy, compilers. Managing Intermountain rangelands--improvement of range and wildlife habitats: Proceedings of symposia; 1981 September 15-17; Twin Falls, ID; 1982 June 22-24; Elko, NV. Gen. Tech. Rep. INT-157. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 83-89. [9652] 20. Nelson, Jack Raymond. 1961. Composition and structure of the principal woody vegetation types in the North Dakota Badlands. Fargo, ND: North Dakota State University. 195 p. Thesis. [161] 21. Pechanec, Joseph F.; Plummer, A. Perry; Robertson, Joseph H.; Hull, A. C., Jr. 1965. Sagebrush control on rangelands. Agriculture Handbook No. 277. Washington, DC: U.S. Department of Agriculture. 40 p. [1858] 22. 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] 23. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 24. Sheehy, Dennis P.; Winward, A. H. 1981. Relative palatability of seven Artemisia taxa to mule deer and sheep. Journal of Range Management. 34(5): 397-399. [2128] 25. Shultz, Leila M. 1986. Comparative leaf anatomy of sagebrush: ecological considerations. In: McArthur, E. Durant; Welch, Bruce L., compilers. Proceedings--symposium on the biology of Artemisia and Chrysothamnus; 1984 July 9-13; Provo, UT. Gen. Tech. Rep. INT-200. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 253-264. [2140] 26. Shultz, Leila M. 1986. Taxonomic and geographic limits of Artemisia subgenus tridentatae (Beetle). In: McArthur, E. Durant; Welch, Bruce L., compilers. Proceedings--symposium on the biology of Artemisia and Chrysothamnus; 1984 July 9-13; Provo, UT. Gen. Tech. Rep. INT-200. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 20-28. [2141] 27. Tisdale, E. W.; Hironaka, M. 1981. The sagebrush-grass region: a review of the ecological literature. Bull. 33. Moscow, ID: University of Idaho, Forest, Wildlife and Range Experiment Station. 31 p. [2344] 28. Volland, Leonard A.; Dell, John D. 1981. Fire effects on Pacific Northwest forest and range vegetation. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region, Range Management and Aviation and Fire Management. 23 p. [2434] 29. Walton, Todd Patrick. 1984. Reproductive mechanisms of plains silver sagebrush Artemisia cana cana in southeastern Montana. Bozeman, MT: Montana State University. 161 p. Thesis. [100] 30. Ward, George H. 1953. Artemisia, section Seriphidium, in North America: a cytotaxonomic study. Contributions from the Dudley Herberium. Stanford, CA: Stanford University, Natural History Museum; 4(6): 155-205. [2454] 31. 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, Office of Biological Services, Western Energy and Land Use Team. 347 p. Available from NTIS, Springfield, VA 22161; PB-83-167023. [2458] 32. White, Richard S.; Currie, Pat O. 1983. The effects of prescribed burning on silver sagebrush. Journal of Range Management. 36(5): 611-613. [2540] 33. White, Richard S.; Currie, Pat O. 1984. Phenological development and water relations in Plains silver sagebrush. Journal of Range Management. 37(6): 503-507. [2542] 34. Wright, Henry A.; Neuenschwander, Leon F.; Britton, Carlton M. 1979. The role and use of fire in sagebrush-grass and pinyon-juniper plant communities: A state-of-the-art review. Gen. Tech. Rep. INT-58. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Statio. 48 p. [2625] 35. Winward, Alma H. 1980. Taxonomy and ecology of sagebrush in Oregon. Station Bulletin 642. Corvallis, OR: Oregon State University, Agricultural Experiment Station. 15 p. [2585] 36. Young, James A.; Evans, Raymond A.; Major, Jack. 1977. Sagebrush steppe. In: Barbour, Michael G.; Major, Jack, eds. Terrestrial vegetation of California. New York: John Wiley & Sons: 763-796. [4300] 37. Young, Richard P. 1983. Fire as a vegetation management tool in rangelands of the Intermountain Region. In: Monsen, Stephen B.; Shaw, Nancy, compilers. Managing Intermountain rangelands--improvement of range and wildlife habitats: Proceedings; 1981 September 15-17; Twin Falls, ID; 1982 June 22-24; Elko, NV. Gen. Tech. Rep. INT-157. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 18-31. [2681] 38. Shultz, Leila M. 1986. [Letter to Nancy McMurray]. March 2. 1 leaf. On file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT; RWU 4403 files. [19700] 39. 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] 40. 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]

Index

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