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Introductory

SPECIES: Mahonia repens | Oregon-Grape
ABBREVIATION : MAHREP SYNONYMS : Berberis repens Lindl. SCS PLANT CODE : MARE BERE COMMON NAMES : Oregon-grape creeping barberry hollygrape creeping mahonia TAXONOMY : The currently accepted scientific name for Oregon-grape is Mahonia repens (Lindl.) G. Don. Recognized varieties and forms are [72]: M. repens var. macrocarpa Jouin. (bigberry Oregon-grape) M. repens var. rotundifolia (May) Jouin. (roundleaf Oregon-grape) M. repens forma subcordata Rehd. (lapleaf Oregon-grape). Three mahonia species (M. repens, M. aquifolium, and M. pinnata) hybridize readily in gardens [65]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Crystal Walkup, October 1991 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Walkup, Crystal J. 1991. Mahonia repens. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Mahonia repens | Oregon-Grape
GENERAL DISTRIBUTION : Oregon-grape occurs throughout the western United States from western Texas (Guadalupe Mountains), New Mexico, Arizona, and California north to British Columbia and Alberta [46,72]. ECOSYSTEMS : FRES11 Spruce - fir FRES19 Aspen - birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES25 Larch FRES26 Lodgepole pine FRES29 Sagebrush STATES : AZ CA CO ID MT ND NE NV NM OR SD TX UT WA WY AB BC ADMINISTRATIVE UNITS : BAND BIHO BICA BLCA BRCA CACH CARE CACA CEBR COLM DETO DINO FOBU GLAC GLCA GRCA GRTE GUMO MEVE NABR NOCA ROMO SUCR THRO TICA WACA YELL ZION BLM PHYSIOGRAPHIC REGIONS : 2 Cascade Mountains 4 Sierra Mountains 5 Columbia Plateau 6 Upper 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 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K008 Lodgepole pine - subalpine forest K010 Ponderosa shrub forest K011 Western ponderosa forest K012 Douglas-fir forest K015 Western spruce - fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K020 Spruce - fir - Douglas-fir forest K023 Juniper - pinyon woodland K038 Great Basin sagebrush SAF COVER TYPES : 16 Aspen 42 Bur oak 210 Interior Douglas-fir 211 White fir 212 Western larch 213 Grand fir 215 Western white pine 217 Aspen 218 Lodgepole pine 220 Rocky Mountain juniper 229 Pacific Douglas-fir 230 Douglas-fir - western hemlock 237 Interior ponderosa pine 238 Western juniper 239 Pinyon - juniper 243 Sierra Nevada mixed conifer 244 Pacific ponderosa pine - Douglas-fir 245 Pacific ponderosa pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Oregon-grape frequency becomes greater in moist habitats. The Oregon-grape phase of the Douglas-fir (Pseudotsuga menziesii)/Oregon-grape habitat types in Idaho is restricted to leeward aspects where site protection and deep soils permit development of a closed tree canopy. Taller shrubs are eventually suppressed, leaving Oregon-grape dominant [61]. Oregon-grape occurs is dominant or subdominant in the following habitat type, plant association, and community type classifications: A classification of forest habitat types of the northern portion of the Cibola National Forest, New Mexico [1] Classification of the forest vegetation of Wyoming [2] Classification of the forest vegetation on the National Forests of Arizona and New Mexico [3] Preliminary plant associaions of the Siskiyou Mountain Province [8] Classification and management of riparian and wetland sites in central and eatern Montana [27] The vegetation of the Grand River/Cedar River, Sioux, and Ashland Districts of the Custer National Forest: a habitat type classification [26] Forest vegetation of the Gunnison and parts of the Uncompahgra National Forests: a preliminary habitat type classification [36] Forest and woodland types (plant assocations) of northern New Mexico and northern Arizona [38] Preliminary riparian community type classification for Nevada [42] Coniferous forest habitat types of northern Utah [43] The Douglas-fir/mountain maple habitat type in central Idaho: succession and management [59] The grand fir/mountain maple habitat type in central Idaho: succession and management [60] Plant assocation and management guide for the grand fir zone, Gifford Pinchot National Forest [69] Big sagebrush (Artemisia tridentata vaseyana) plant associations in northeatern Nevada [70].

VALUE AND USE

SPECIES: Mahonia repens | Oregon-Grape
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Oregon-grape fruits are eaten by a number of bird and mammal species, including black bears [72]. Season of use determines the amount of foliage browsed by mule deer, white-tailed deer, and elk. Moose and bighorn sheep make little use of the plants regardless of the season [53,63,68], but it provides a winter food source for mule and white-tailed deer in the Black Hills of South Dakota [23,31]. Mule deer use is high in the fall and winter in Montana and Nevada [25,35], and low in the summer in Utah [57]. In Idaho it provides an important spring browse for white-tailed deer and elk [34,40]. Oregon-grape may be poisonous to livestock; they make virtually no use of the plants [16,72]. PALATABILITY : NO-ENTRY NUTRITIONAL VALUE : Oregon-grape browse has only fair food value. Protein contents range from 4.7 to 5.5 percent. It provides a high source of carotene in July [23]. COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : Oregon-grape is currently used for landscaping and xeriscaping because it provides evergreen ground cover that is both heat and drought tolerant [62,73,74]. Though sometimes browsed by deer, it generally recovers during the growing season [33]. Game rangelands, old mines, roadsides, and recreation areas are suggested sites for planting this species. Oregon-grape should comprise 10 to 25 percent of a seed mixture for these uses. Successful stand establishment requires reduction of competing vegetation before and during establishment [73]. Plants are propagated by seeds, suckers, cuttings, and layering [72]. Seeding or transplanting in rows, strips, or blocks may improve stand establishment and survival. A seeding rate of 10 to 20 pure live seeds per square foot is recommended for full stands. Seeds can be sown in the fall without treatment, but they require stratification prior to planting in the spring [54,73]. Transplanting rootstocks is possible but difficult in less humid, interior climates [73]. OTHER USES AND VALUES : Dye: Navajo Indians produced a yellow dye from the roots and a lavender dye from the fruit [46]. Medicinal: Great Basin tribes used tea obtained by boiling the roots for thickening blood and curing dysentery. The tea was considered efficacious for curing coughs, kidney problems, and venereal diseases [46]. Food: Preserves, drinks, and pies are made from the berries [46]. MANAGEMENT CONSIDERATIONS : Oregon-grape shows little change after silvicultural treatments such as clearcutting and mechanical scarification [7]. Oregon-grape has low short-term resistance to trampling by people but recovers steadily if trampling is eliminated for long periods. Overall, it is considered moderately resistant to trampling since it does recover [15]. Oregon-grape is an alternate host for black stem rust, a serious pathogen of cereal crops, and should not be planted where cereal crops are grown [29,72].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Mahonia repens | Oregon-Grape
GENERAL BOTANICAL CHARACTERISTICS : Oregon-grape is a native, evergreen, perennial shrub with a low or prostrate growth form [46]. Stem heights of 4 to 12 inches (10 to 30 cm) are common [63,72]. Each stem arises from a rhizome [46,63,72]. Roots have been observed extending to 6 feet (1.8 m) without being concentrated at any depth, suggesting a long taproot that would make it adaptable to a wide variety of sites [47]. The leaves are pinnately compound and spine-tipped, and the berries are born in grapelike clusters [72]. RAUNKIAER LIFE FORM : Chamaephyte REGENERATION PROCESSES : Sexual: Oregon-grape flowers are cross-pollinated by bees, but those not receiving pollen from another source are selfed. Selfing frequently does not result in fruit production [46], but good fruit crops are borne almost annually from cross-pollinated plants. Wildlife consume the berries and may aid in seed dispersal. Seed can remain viable for up to 5 years in sealed containers stored in unheated sheds [49]. Vegetative: Vegetative growth is initiated from horizontally growing rhizomes, found 0.5 to 2 inches (1.2-5 cm) below the mineral soil [46,49,62]. SITE CHARACTERISTICS : Oregon-grape grows on thinly wooded slopes or shaded hillsides in rocky, slightly moist soil, or occasionally on open hillsides [63]. It is among the most resistant plants to leaf burn from exposure to the winter sun [73]. Soils: Oregon-grape is found on sandy loams to silts, sedimentary shales and sandstones, and granitic soils in coniferous forests [46,63,72]. In western Montana it is found on limestone soils and is absent or nearly so on granitic and quartzite soils [24]. In the Black Hills it is confined to calcareous soils developed from limestone parent material [66]. Elevation: Oregon-grape has a wide elevation range, from near sea level on the Pacific Coast to 10,000 feet (3,048 m)in the Rocky Mountains [72]. It is found in high-elevation coniferous forests throughout the Great Basin [46]. Elevations in Utah range from 4,000 to 9,800 feet (1,125-2,980 m) [74]. Major overstory associates include ponderosa pine (Pinus ponderosa), Douglas-fir, grand fir (Abies grandis), quaking aspen (Populus tremuloides), and western larch (Larix occidentalis). Major understory associates include snowberry (Symphoricarpos alba), Rocky Mountain maple (Acer glabrum), twinflower (Linnaea borealis), blue huckleberry (Vaccinium globulare), dwarf huckleberry (V. scoparium), and ninebark (Physocarpus malvaceus) [10]. SUCCESSIONAL STATUS : Facultative Seral Species Oregon-grape is a climax dominant which is shade-tolerant, but also does well in full sunlight [51]. In the cedar-hemlock (Thuja spp./Tsuga spp.) zone, it initially responds to open canopies produced by logging, but begins to decrease within 25 years [75]. Oregon-grape is the dominant shrub in closed canopy stands of Douglas-fir [61]. SEASONAL DEVELOPMENT : In the northern Rocky Mountains Oregon-grape first develops new leaves from the end of April until late May. Flowering starts in early May and may extend to early August. Fruit ripens from late June until mid-September [55]. In South Dakota and Nebraska, flowering occurs in early June, and fruit is ripe by late August [63].

FIRE ECOLOGY

SPECIES: Mahonia repens | Oregon-Grape
FIRE ECOLOGY OR ADAPTATIONS : Oregon-grape is adapted to fire and survives by sprouting from dormant buds on the rhizomes [45]. Seedling establishment occurs from on-site seed [48]. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud root crown Ground residual colonizer (on-site, initial community)

FIRE EFFECTS

SPECIES: Mahonia repens | Oregon-Grape
IMMEDIATE FIRE EFFECT ON PLANT : Oregon-grape usually survives all but severe fires that remove duff and cause extended heating of the upper soil [17,48]. One study reported that a severe fire favored Oregon-grape [11], but fire conditions were not specified. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Oregon-grape was absent after severe fires in northern Idaho but unharmed by moderate fires [6]. Density and height increases have been noted in the second postfire growing season [48]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : Five years following a moderate- to high-intensity fire, Oregon-grape reached 60 percent of prefire biomass in a mixed aspen/conifer stand, 65 percent in an upper elevation aspen stand, and 85 percent in a lower elevation aspen stand [12]. Four different fires were studied to determine successional responses of Oregon-grape following fire. At postfire year 1 cover had decreased, remained the same at postfire year 2, decreased in postfire year 9, and was much higher at postfire year 18. Fire severity may be related to the survival of Oregon-grape. Generally, an increase in cover should occur by 9 postfire years [44]. Oregon-grape cover increased during postfire years 1 and 2 following an April fire in western Montana. It invaded an burn resulting from an October fire during the second postfire year [48]. FIRE MANAGEMENT CONSIDERATIONS : Oregon-grape may be supressed in areas seeded to grass following wildfires. This should be considered before planting grasses in areas where Oregon-grape is an important food for wildlife [5]. Prescribed fire has a low probability of success in the aspen/low forb community type, of which Oregon-grape is a main component, because of the sparse vegetation [13].

REFERENCES

SPECIES: Mahonia repens | Oregon-Grape
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A preliminary study of the vegetation in an exclosoure in the chaparral of the Wasatch Mountains, Utah. Utah Academy Proceedings. 30: 63-78. [9096] 5. Anderson, E. William; Brooks, Lee E. 1975. Reducing erosion hazard on a burned forest in Oregon by seeding. Journal of Range Management. 28(5): 394-398. [12807] 6. Armour, Charles D.; Bunting, Stephen C.; Neuenschwander, Leon F. 1984. Fire intensity effects on the understory in ponderosa pine forests. Journal of Range Management. 37(1): 44-48. [6618] 7. Arno, Stephen F.; Simmerman, Dennis G.; Keane, Robert E. 1985. Forest succession on four habitat types in western Montana. Gen. Tech. Rep. INT-177. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 74 p. [349] 8. Atzet, Thomas; Wheeler, David L. 1984. Preliminary plant associations of the Siskiyou Mountain Province. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 278 p. [9351] 9. 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] 10. Berner, Kevin L.; Fiedler, Carl E.; Pletscher, Daniel H. 1988. White-tailed deer winter habitat use in western Montana second-growth forests. Res. Rep. No. 2. Missoula, MT: University of Montana, Montana Forest and Conservation Experiment Station. 7 p. [6917] 11. Blaisdell, James P. 1953. Ecological effects of planned burning of sagebrush-grass range on the upper Snake River Plains. Tech. Bull. 1975. Washington, DC: U.S. Department of Agriculture. 39 p. [462] 12. Brown, James K.; DeByle, Norbert V. 1989. Effects of prescribed fire on biomass and plant succession in western aspen. Res. Pap. INT-412. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 16 p. 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Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 77 p. Preliminary draft. [8434] 60. Steele, Robert; Geier-Hayes, Kathleen. 1989. The grand fir/mountain maple habitat type in central Idaho: succession and management. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 148 p. Review draft. [8435] 61. Steele, Robert; Pfister, Robert D.; Ryker, Russell A.; Kittams, Jay A. 1981. Forest habitat types of central Idaho. Gen. Tech. Rep. INT-114. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 138 p. [2231] 62. Steffey, Jane. 1985. Strange relatives: the barberry family. American Horticulturalist. 64(4): 4-9. [10354] 63. Stephens, H. A. 1973. Woody plants of the North Central Plains. Lawrence, KS: The University Press of Kansas. 530 p. [3804] 64. Stevens, David R. 1970. Winter ecology of moose in the Gallatin Mountains, Montana. 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Related categories for Species: Mahonia repens | Oregon-Grape

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