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Introductory

SPECIES: Holodiscus dumosus | Bush Oceanspray
ABBREVIATION : HOLDUM SYNONYMS : Holodiscus microphyllus Rydb. Holodiscus discolor var. microphyllus (Rydb.) Jepson Holodiscus discolor var. dumosa (Nutt.) Dippel Sericotheca dumosa (Nutt.) Rydb. SCS PLANT CODE : HODU COMMON NAMES : bush oceanspray mountain spray rock spray spirea bush rockspirea mountain-spray gland oceanspray TAXONOMY : The fully documented scientific name of bush oceanspray is Holodiscus dumosus (Nutt.) Heller. The taxonomy presented here follows that of Welsh and others [36]. These authors take a conservative approach to recognizing infraspecific taxa within this complex, indicating that most variation appears to reflect ecological rather than genetic differences. Holodiscus microphyllus, an entity occurring in montane habitats from Oregon to California [21,25], has been included within Holodiscus dumosus [14,15,36]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : N. McMurray/ October 1987 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : McMurray, Nancy E. 1987. Holodiscus dumosus. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Holodiscus dumosus | Bush Oceanspray
GENERAL DISTRIBUTION : Bush oceanspray occurs from north-central Oregon east to Wyoming and southward throughout much of the Great Basin to California, Nevada, Arizona, New Mexico, and Chihuahua, Mexico [14,36]. Along the western edge of its range, this species occurs essentially east of the Cascade Range, extending southward to northwestern California and the central Sierra Nevada [14,25]. ECOSYSTEMS : FRES20 Douglas-fir FRES21 Ponderosa pine FRES23 Fir - spruce FRES29 Sagebrush FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES40 Desert grasslands STATES : AZ CA CO ID NV NM OR UT WY Mexico ADMINISTRATIVE UNITS : BAND BLCA BRCA CANY CARE CACA CHIR COLM CRMO DINO FOBU GRCA GRBA GRSA GUMO MEVE NABR ROMO SAGU SUCR TICA YOSE ZION BLM PHYSIOGRAPHIC REGIONS : 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 KUCHLER PLANT ASSOCIATIONS : K004 Fir - hemlock forest K005 Mixed conifer forest K011 Western ponderosa forest K012 Douglas-fir forest K015 Western spruce - fir forest K018 Pine - Douglas-fir forest K019 Arizona pine forest K021 Southwestern spruce - fir forest K022 Great Basin pine forest K023 Juniper - pinyon woodland K024 Juniper steppe woodland K034 Montane chaparral K037 Mountain-mahogany - oak scrub K038 Great Basin sagebrush K055 Sagebrush steppe K057 Galleta - three-awn shrubsteppe SAF COVER TYPES : 205 Mountain hemlock 206 Engelmann spruce - subalpine fir 207 Red fir 208 Whitebark pine 209 Bristlecone pine 210 Interior Douglas-fir 211 White fir 216 Blue spruce 219 Limber pine 237 Interior ponderosa pine 238 Western juniper 239 Pinyon - juniper 243 Sierra Nevada mixed conifer 256 California mixed subalpine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Bush oceanspray has been used as an indicator of climax conditions on rocky sites in both nonforested and forested communities throughout its range. A bush oceanspray shrubland series has been described for steep, talus slopes in Colorado; habitat types include bush oceanspray/Thurber fescue (Festuca thurberi) and bush oceanspray/wax current (Ribes cereum) [17]. In the Pacific Northwest, Erhard [7] has described a curlleaf mountain-mahogany/bush oceanspray (Cercocarpus ledifolius/Holodiscus microphyllus var. glabrescens) habitat type associated with basalt lava flows. Along the east slope of the Cascades in Oregon, Hopkins and Kovalchik [16] have described a western juniper/big sagebrush-bush oceanspray/bluebunch wheatgrass-arrowleaf (Juniperus occidentalis/ Artemisia tridentata-Holodiscus dumosa/Pseudoroegneria spicata- Balsamorhiza sagittata) community type. On high-elevation sites in the southern Rocky Mountains, bush oceanspray is listed as the understory dominant in forested scree habitat types within the white fir (Abies concolor), alpine fir (A. lasiocarpa), and Douglas-fir (Pseudotsuga menzeisii) series; it is also utilized as a phase indicator in the following Southwestern forested habitat types [1]: white fir/big tooth maple (Acer grandidentatum) white fir/Rocky mountain maple (A. glabrum) white fir/Gambel oak (Quercus gambelii) Douglas-fir/Gambel oak white fir-Douglas-fir/Rocky Mountain maple Published classifications listing bush oceanspray as a climax indicator are listed below. A classification of forest habitat types of northern New Mexico and southern Colorado. [4] A classification of forest habitat types of the Lincoln National Forest, New Mexico. [1] A classification of spruce-fir and mixed conifer habitat types of Arizona and New Mexico. [23] Forest vegetation of the Gunnison and parts of the Uncompahgre National Forests: a preliminary habitat type classification. [19] Plant associations of the Crooked River National Grassland, Ochoco National Forest. [16] Plant associations of Region Two. [17] Plant communities and habitat types in the Lava Beds National Monument, California. [7]

VALUE AND USE

SPECIES: Holodiscus dumosus | Bush Oceanspray
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Bush oceanspray is generally unpalatable to the majority of livestock and big game [32]. It increases in response to grazing on western juniper/big sagebrush habitat types in eastern Oregon [16]. Since this species is typically distributed on the summer ranges of most animals, Ferguson [10] suggests that bush oceanspray is not an extensively utilized browse plant. In southern Colorado, however, bush oceanspray comprises a portion of the summer diet of bighorn sheep [31]. PALATABILITY : Bush oceanspray is generally unpalatable to both livestock and big game [32]. However, it comprised an average relative density of 10 percent of the summer diet of bighorn sheep populations in southern Colorado. Plants are utilized by a variety of small bird species [30], and also by rabbits in California [34]. The palatability of bush oceanspray to livestock and wildlife species in several western states has been rated as follows [5]: CO UT WY Cattle Poor Poor ---- Sheep Poor Fair ---- Horses Poor Poor ---- Pronghorn ---- Poor Poor Elk Poor Poor Poor Mule deer Poor Fair Fair White-tailed deer ---- ---- Fair Small mammals ---- Fair ---- Small nongame birds ---- Fair Fair Upland game birds ---- Fair ---- Waterfowl ---- Poor ---- NUTRITIONAL VALUE : Bush oceanspray has been rated as fair in both energy and protein value [5]. COVER VALUE : The degree to which bush oceanspray provides environmental protection during one or more seasons for wildlife species has been rated as follows [5]: CO UT WY Pronghorn ---- Poor Poor Elk ---- Fair Fair Mule deer Poor Fair Good White-tailed deer ---- ---- Good Small mammals Fair Fair Good Small nongame birds Fair Fair Good Upland game birds ---- Fair Good Waterfowl ---- Poor Poor VALUE FOR REHABILITATION OF DISTURBED SITES : Bush oceanspray appears to be an excellent candidate for use in the reclamation of disturbed sites within its range. Plants are naturally capable of establishing and persisting on rather severe, rocky sites [6,7] and are also extremely drought tolerant [28]. In additon, this species is adapted to sites with unstable, shifting surface materials; it is often the dominant species on sites characterized by moving screes in both nonforested [17,18] and forested [4] communities. Despite such attributes, bush oceanspray has not been widely used in rehabilitation projects, primarily due to a scarcity of commercially available seed [10,26,28]. Other factors contributing to problems in the culture of the Holodiscus genus include: (1) a pronounced seed dormancy and (2) low production of viable seed [29,35]. Stickney [29] reported that germination of oceanspray (Holodiscus discolor) is enhanced following stratification at 41 degrees Fahrenheit (15 deg C) for 18 weeks. Although plants can be successfully established via fall broadcast seeding, nursery culture from fall-sown seed appears to be a more reliable means of propagation; fall-planted bareroot stock is generally quite hardy [28]. Propagating Holodiscus accessions via stem cuttings has been unsuccessful in Nevada [8]. The adaptability of bush oceanspray to high-elevation mountain sites has been rated as follows [26]: Adaptational attribute Rating (1-5) ---------------------- -------------- Established by seed medium (3) Established by transplant medium (3) Seed production & handling medium (3) Natural spread (seed) good (4) Natural spread (vegetative) medium (3) Growth rate good (4) Soil stablility good (4) Adaptation to disturbance good (4) OTHER USES AND VALUES : East of the Cascade Range, bush oceanspray is planted as a showy ornamental shrub [28,30]; plants are often preferred to oceanspray due to their more compact growth form [14]. Indigenous peoples used the extremely hard wood of this shrub to make arrows and digging sticks; pioneers used it to make nails [16]. The "berries" were once gathered as food by Indian tribes inhabiting the Great Basin [2]. MANAGEMENT CONSIDERATIONS : NO-ENTRY

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Holodiscus dumosus | Bush Oceanspray
GENERAL BOTANICAL CHARACTERISTICS : Bush oceanspray is a moderately long-lived, native, deciduous, drought-tolerant shrub that typically ranges from 20 to 60 inches (25-150 cm) in height [14,25,28,36]. Plants are densely to intricately branched from the base. The majority of the foliage originates on spur branches with leaves in fasicles of six or seven [14]. The root system is fibrous and spreading [28]. This species is characteristically found in large clumps [34]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Information on the regenerative processes of bush oceanspray is scant. Plummer [26] reported that this species possessed an above average capacity to spread naturally via wind-dispersed seed on disturbed sites in Utah; however, seedling establishment is rated as only average. Bush oceanspray has a high resistance to disturbance, but modes of vegetative regeneration have not been widely documented or described. For a description of the regeneration processes of a morphologically and ecologically similar ally, see the FEIS write-up for oceanspray (Holodiscus discolor). SITE CHARACTERISTICS : Bush oceanspray is most often associated with dry, rocky habitats [32]. In the Great Basin this shrub is ubiquitous in numerous plant communities from desert valleys to areas well up in the mountains [14]; it is most abundant at elevations between 4,500 and 11,000 feet (1,372 and 3,354 m) [24]. Typical sites include rocky outcrops, slickrock plateau margins, bases of cliffs, talus slopes, and steep, canyon walls [36]. Soils are dry to moderately dry, and well drained; textures range from sand to clay [28]. Plants appear somewhat tolerant of alkaine soils. Elevational ranges vary as follows [5,16,25]: from 6,800 to 10,000 feet (2,073-3,049 m) in AZ 5,500 to 11,000 feet (1,677-3,354 m) in CA 5,500 to 10,000 feet (1,677-3,049 m) in CO 7,200 to 8,500 feet (2,195-2,591 m) in NM 2,500 to 3,000 feet (726-915 m) in OR 4,198 to 12,000 feet (1,280-3,659 m) in UT 6,500 to 8,200 feet (1,982-2,500 m) in WY SUCCESSIONAL STATUS : Self-perpetuating stands of bush oceanspray are indicative of climax conditions on rocky sites in both nonforested and forested communities [4,16]. This species is a pioneer on young lavas in southern Idaho. Plants establish during early seral stages and coexist with later arriving species that are also adapted to such severe site conditions [6]. Bush oceanspray is a component of seral brushfields that develop following fire on white fir/Rocky Mountain maple/bush oceanspray sites in New Mexico [1,13]. However, it is unclear whether postburn coverages are derived via residual plant survival or from seedling establishment. SEASONAL DEVELOPMENT : Bush oceanspray generally begins blooming in June at lower elevations in the Great Basin, but on sites at the upper limits of its elevational range, plants may not flower until August [24]. Anthesis data for several western states are as follows [5,25,36]: State Earliest flowering Latest Flowering date date ------------------ ---------------- CA June August CO June August UT June August WY July September

FIRE ECOLOGY

SPECIES: Holodiscus dumosus | Bush Oceanspray
FIRE ECOLOGY OR ADAPTATIONS : The fire ecology and fire adaptations of bush oceanspray are poorly documented. Fire is reported to be the principal factor initiating succession on many of the high-elevation sites occupied by this shrub in the Southwest [12], and bush oceanspray is apparently able to maintain itself into late successional stage on many of these rocky, forested sites [1]. It is currently unknown whether postfire reestablishment is from sprouting from surviving plants, or from on-site or off-site seed sources, or both. In the White Mountains of New Mexico, bush oceanspray was a conspicuous componenet of the shrub layer 2 to 3 years after fire [13]. POSTFIRE REGENERATION STRATEGY : Initial-offsite colonizer (off-site, initial community) Small shrub, adventitious-bud root crown Ground residual colonizer (on-site, initial community)

FIRE EFFECTS

SPECIES: Holodiscus dumosus | Bush Oceanspray
IMMEDIATE FIRE EFFECT ON PLANT : The effect of fire on bush oceanspray is poorly documented. The intricately branched nature of this shrub suggests that most plants are readily top-killed by relatively low-intensity fires. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Fire response of bush oceanspray is poorly documented. A similar species, oceanspray (H. discolor), increases by prolific sprouting. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Holodiscus dumosus | Bush Oceanspray
REFERENCES : 1. Alexander, Billy G., Jr.; Ronco, Frank, Jr.; Fitzhugh, E. Lee; Ludwig, John A. 1984. A classification of forest habitat types of the Lincoln National Forest, New Mexico. Gen. Tech. Rep. RM-104. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 29 p. [300] 2. Andersen, Berniece A.; Holmgren, Arthur H. [n.d.]. Mountain plants of northeastern Utah. Circular 319. Logan, UT: Utah State University, Extension Services. 148 p. [312] 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. DeVelice, Robert L.; Ludwig, John A.; Moir, William H.; Ronco, Frank, Jr. 1986. A classification of forest habitat types of northern New Mexico and southern Colorado. Gen. Tech. Rep. RM-131. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 59 p. [781] 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. Eggler, Willis A. 1941. Primary succession on volcanic deposits in southern Idaho. Ecological Monographs. 11: 277-298. [852] 7. Erhard, Dean H. 1979. Plant communities and habitat types in the Lava Beds National Monument, California. Corvallis, OR: Oregon State University. 173 p. Thesis. [869] 8. 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] 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. Ferguson, Robert B. 1983. Use of rosaceous shrubs for wildland plantings in the Intermountain West. 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: 136-149. [915] 11. 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] 12. Hanks, Jess Paul. 1966. Vegetation of the mixed conifer zone; White Mountains, New Mexico. University Park, NM: New Mexico State University. 39 p. Thesis. [4632] 13. Hanks, Jess P.; Dick-Peddie, W. A. 1974. Vegetation patterns of the White Mountians, New Mexico. Southwestern Naturalist. 18(4): 371-382. [4635] 14. Hitchcock, C. Leo; Cronquist, Arthur. 1961. Vascular plants of the Pacific Northwest. Part 3: Saxifragaceae to Ericaceae. Seattle, WA: University of Washington Press. 614 p. [1167] 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. Hopkins, William E.; Kovalchik, Bernard L. 1983. Plant associations of the Crooked River National Grassland. R6 Ecol 133-1983. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 98 p. [1193] 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. Komarkova, Vera. 1986. Habitat types on selected parts of the Gunnison and Uncompahgre National Forests. Final Report Contract No. 28-K2-234. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 270 p. [1369] 19. Komarkova, Vera; Alexander, Robert R.; Johnston, Barry C. 1988. Forest vegetation of the Gunnison and parts of the Uncompahgre National Forests: a preliminary habitat type classification. Gen. Tech. Rep. RM-163. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 65 p. [5798] 20. 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] 21. Ley, Arline. 1943. A taxonomic revision of the genus Holodiscus (Rosaceae). Bulletin of the Torrey Botanical Club. 70(3): 275-288. [142] 22. 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] 23. Moir, William H.; Ludwig, John A. 1979. A classification of spruce-fir and mixed conifer habitat types of Arizona and New Mexico. Res. Pap. RM-207. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 47 p. [1677] 24. Mozingo, Hugh N. 1987. Shrubs of the Great Basin: A natural history. Reno, NV: University of Nevada Press. 342 p. [1702] 25. Munz, Philip A. 1973. A California flora and supplement. Berkeley, CA: University of California Press. 1905 p. [6155] 26. Plummer, A. Perry. 1976. Shrubs for the subalpine zone of the Wasatch Plateau. In: Zuck, R. H.; Brown, L. F., eds. High altitude revegetation workshop: No. 2: Proceedings; 1976; Fort Collins, CO. Fort Collins, CO: Colorado State University: 33-40. [1899] 27. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 28. Stark, N. 1966. Review of highway planting information appropriate to Nevada. Bull. No. B-7. Reno, NV: University of Nevada, College of Agriculture, Desert Research Institute. 209 p. In cooperation with: Nevada State Highway Department. [47] 29. Stickney, Peter F. 1974. Holodiscus discolor (Pursh) Maxim. creambush rockspiraea. In: Schopmeyer, C. S., ed. Seeds of woody plants in the United States. Agriculture Handbook No. 450. Washington, DC: U.S. Department of Agriculture, Forest Service: 448-449. [7682] 30. Sutton, Richard F.; Johnson, Craig W. 1974. Landscape plants from Utah's mountains. EC-368. Logan, UT: Utah State University, Cooperative Extension Service. 135 p. [49] 31. Todd, J. W. 1975. Foods of Rocky Mountain bighorn sheep in southern Colorado. Journal of Wildlife Management. 39(1): 108-111. [6218] 32. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 33. 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] 34. Van Dersal, William R. 1938. Native woody plants of the United States, their erosion-control and wildlife values. Washington, DC: U.S. Department of Agriculture. 362 p. [4240] 35. Vories, Kimery C. 1981. Growing Colorado plants from seed: a state of the art. Volume I. Shrubs. Gen. Tech. Rep. INT-103. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 80 p. [3426] 36. 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] 37. Wright, Henry A.; Bailey, Arthur W. 1982. Fire ecology: United States and southern Canada. New York: John Wiley & Sons. 501 p. [2620]

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