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Introductory

SPECIES: Opuntia humifusa | Eastern Prickly-Pear
ABBREVIATION : OPUHUM SYNONYMS : Opuntia compressa (Salisb.) Macbr. Opuntia mesacantha Raf. SCS PLANT CODE : OPHU COMMON NAMES : eastern prickly-pear cactus TAXONOMY : The currently accepted scientific name of eastern prickly-pear cactus is Opuntia humifusa (Raf.) Raf. [2,13]. Recognized varieties are as follows: O. h. var. ammophilia (Small) L. Benson [2,16] O. h. var. austrina (Small) Dress [16,26] O. h. var. fusco-atra (Eng.) Winiger [19] O. h. var. humifusa [2,16] Eastern prickly-pear cactus hybridizes with O. pusilla, O. vulgaris, O. stricta var. stritca, and O. stritca var. dillenii [2]. LIFE FORM : Cactus FEDERAL LEGAL STATUS : No special status OTHER STATUS : Eastern prickly-pear cactus is listed as endangered in Ontario [31]. COMPILED BY AND DATE : Janet L. Howard, June 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Howard, Janet L. Opuntia humifusa. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Opuntia humifusa | Eastern Prickly-Pear
GENERAL DISTRIBUTION : Eastern prickly-pear cactus occurs in the Midwest, East, South, and Southwest. It is distributed across South Dakota, Minnesota, and southernmost Ontario to Massachusetts and south to the Gulf States, Colorado, New Mexico, Arizona, and Mexico [10,13,14]. Disjunct populations occur near Great Falls, Montana, and in Utah County, Utah [2]. ECOSYSTEMS : FRES13 Loblolly - shortleaf pine FRES15 Oak - hickory FRES16 Oak - gum - cypress FRES18 Maple - beech - birch FRES29 Sagebrush FRES30 Desert shrub FRES31 Shinnery FRES32 Texas savanna FRES33 Southwestern shrubsteppe FRES35 Pinyon - juniper FRES38 Plains grasslands FRES39 Prairie FRES40 Desert grasslands STATES : AK AZ AR CO CT DE FL GA IL IN IA KS KY LA MD MA MI MN MS MO MT NE NH NJ NC OH OK PA RI SC SD TN TX UT VT VA WV WI ON MEXICO ADMINISTRATIVE UNITS : ASIS BAND BITH BLRI BUFF CACO CAHA CALO CHCH COLO CUIS DEWA EVER FIIS GATE GWMP GUMO GUIS HOBE HOSP INDU MACA NATR OBRI PAIS PIPE RICH ROMO WICR WICA BLM PHYSIOGRAPHIC REGIONS : 7 Lower Basin and Range 12 Colorado Plateau 13 Rocky Mountain Piedmont 14 Great Plains 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K023 Juniper - pinyon woodland K027 Mesquite bosque K038 Great Basin sagebrush K039 Blackbrush K040 Saltbush - greasewood K044 Creosote bush - tarbush K045 Ceniza shrub K046 Desert: vegetation largely lacking K053 Grama - galleta steppe K054 Grama - tobosa prairie K058 Grama - toboas shrubsteppe K059 Trans-Pecos shrub savanna K060 Mesquite savanna K062 Mesquite - live oak savanna K065 Grama - buffalograss K066 Wheatgrass - needlegrass K067 Wheatgrass - bluestem - needlegrass K068 Wheatgrass - grama - buffalograss K069 Bluestem - grama prairie K070 Sandsage - bluestem prairie K071 Shinnery K072 Sea oats prairie K074 Bluestem prairie K075 Nebraska sandhills prairie K076 Blackland prairie K077 Bluestem - sacahuista prairie K081 Oak savanna K082 Mosaic of K074 and K100 K084 Cross Timbers K085 Mesquite - buffalograss K087 Mesquite - oak savanna K088 Fayette prairie K089 Black Belt K090 Live oak - sea oats K091 Cyress savanna K099 Maple - basswood forest K100 Oak - hickory forest K102 Beech - maple forest K104 Appalachian oak forest K110 Northeastern oak - pine forest K111 Oak - hickory - pine forest K112 Southern mixed forest K114 Pocosin K115 Sand pine scrub SAF COVER TYPES : 24 Hemlock - yellow birch 25 Sugar maple - beech - yellow birch 26 Sugar maple - basswood 27 Sugar maple 40 Post oak - blackjack oak 42 Bur oak 45 Pitch pine 52 White oak - black oak - northern red oak 60 Beech - sugar maple 66 Ashe juniper - redberry (Pinchot) juniper 67 Mohrs ("shin") oak 68 Mesquite 69 Sand pine 71 Longleaf pine - scrub oak 72 Southern scrub oak 74 Cabbage palmetto 75 Shortleaf pine 76 Shortleaf pine - oak 78 Virginia pine - oak 79 Virginia pine 80 Loblolly pine - shortleaf pine 81 Loblolly pine - shortleaf pine 82 Loblolly pine - hardwood 85 Slash pine - hardwood 220 Rocky Mountain juniper 239 Pinyon - juniper 240 Arizona cypress 241 Western live oak 242 Mesquite SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Eastern prickly-pear cactus flourishes in open desert areas where other vegetation is lacking [1]. It is also prominent in seabeach and other dune communities [22,26]. Conover [8] lists eastern prickly-pear cactus as an indicator species of prairie habitat. It has not been listed as an indicator of dominance or subdominance in habitat typings. Associated species: Eastern prickly-pear cactus is not associated with the presence of any one species or genera of other plants, except those also occurring in open areas [2].

VALUE AND USE

SPECIES: Opuntia humifusa | Eastern Prickly-Pear
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : The stems and fruits of eastern prickly-pear are eaten by the ornate box turtle, endangered in Wisconsin [7], various birds, rodents, and lagomorphs [7,28], white-tailed deer [23], and all classes of livestock [28]. Rodents also consume roots and seeds [7,29]. PALATABILITY : The stems of spiny phenotypes are generally preferred by livestock and wildlife species when young, before spines mature [5]. NUTRITIONAL VALUE : Eastern prickly-pear cactus is poor forage for livestock [15]. The nutritional value of fresh, immature eastern prickly-pear stems in the United States is as follows [21]: Percent Composition Percent Digestible Protein ash 2.6 cattle 0.5 crude fiber 1.2 horses 0.4 protein 0.9 rabbits 0.5 sheep 0.5 COVER VALUE : Snakes and lizards use eastern prickly-pear cactus for shade cover. Various birds sometimes nest among the stems, where spines aid in protecting eggs and nestlings from predators [7]. VALUE FOR REHABILITATION OF DISTURBED SITES : Eastern prickly-pear cactus can be useful in wildlife habitat and other restoration projects. An eastern prickly-pear population was established from nursery-germinated seedlings on a sand and gravel borrow-pit reclamation site in Greene County, Ohio [8]. Eastern prickly-pear cactus is also easily established from stem cuttings, which are buried to approximately three-fifths of their length to promote optimum rooting [29]. OTHER USES AND VALUES : Humans eat eastern prickly-pear fruits [2,7]. Native Americans consumed the fresh and dried fruits of eastern prickly-pear cactus, and roasted and ate the stems. The mucilaginous stem sap was used as a wound dressing [12]. MANAGEMENT CONSIDERATIONS : Eastern prickly-pear cactus is sometimes used for emergency forage on depleted ranges. It does not provide a maintenence diet for cattle [15].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Opuntia humifusa | Eastern Prickly-Pear
GENERAL BOTANICAL CHARACTERISTICS : Eastern prickly-pear is a native, low clump- or mat-forming cactus, usually 3 to 4 inches (7.5-10 cm) in height. It occasionally grows to 12 inches (30 cm) in height in Florida. The succulent stems or pads are from 1.5 to 4 inches (3.8-10 cm) long and from 1.6 to 2.4 inches (4-6 cm) wide. Zero to two spines are found on the upper areoles of stems. Fruits are fleshy and persist until spring. The fiberous roots lack prominent tubercules [2,10]. RAUNKIAER LIFE FORM : Hemicryptophyte Stem succulent REGENERATION PROCESSES : Sexual: Eastern prickly-pear cactus reproduces by seed. Seed is disseminated when seed-bearing fruits drop from mature stems in spring [2], or by frugiverous birds and mammals. Clustered populations of eastern prickly-pear are sometimes established when ground squirrels gather seed from animal droppings and store them in caches [28]. Germination is slow in this genus [29]. Flowers are produced at 2 years of age [8], and are pollinated by insects [19]. Vegetative: Eastern prickly-pear cactus reproduces asexually from semiprostrate stems, which root in soil [29]. The genus can sprout from the caudex when the aboveground portion of the plant is destroyed [5]. SITE CHARACTERISTICS : Eastern prickly-pear cactus grows on open, sunny, dry flats or south-facing exposures with up to a 50 degree slope. Soils vary from organic detritus to shale-loam, sandy loam, coastal beachland and Lakewood sand. The species tolerates low-nutrient, acid, and alkaline soils [2]. SUCCESSIONAL STATUS : Facultative Seral Species Eastern prickly-pear cactus colonizes disturbed sites and may persist through late seral stages of plant succession. It colonizes bare coastal dunes in some areas of the Northeast [27]. On the dunes of southern Lake Michigan, it appears in early seral stages, where it invades the beachgrass (Ammophilia breviligulata)-prairie sandreed (Calamovilfa longifolia) communities of young dunes. It is found in late seral, shrub-populated dunes on the shores of western Lake Michigan [22], and in climax sand sage (Artemisia filifolia) communities in northeastern Colorado [24]. It is probably a relict in climax communities, however. Eastern prickly-pear is shade-intolerant [17] and is generally replaced by other species in advanced stages of succession [2]. SEASONAL DEVELOPMENT : Eastern prickly-pear cactus produces flowers and fruits year-round in semiarid regions of the Southwest [19]. In southwestern Wisconsin, flowers appear in June, fruits ripen in late summer and fall, and drop in early spring [7].

FIRE ECOLOGY

SPECIES: Opuntia humifusa | Eastern Prickly-Pear
FIRE ECOLOGY OR ADAPTATIONS : Fire information is lacking for this species. Opuntia spp. sprout from the root crown and from surviving stems following light fire [5]. Prickly pear cactus colonizes burned areas when off-site seed is transported on-site by animals [28]. POSTFIRE REGENERATION STRATEGY : survivor species; on-site surviving root crown off-site colonizer; seed carries by animals or water; postfire yr 1&2 secondary colonizer; off-site seed carried to site after year 2

FIRE EFFECTS

SPECIES: Opuntia humifusa | Eastern Prickly-Pear
IMMEDIATE FIRE EFFECT ON PLANT : Moderate-severity fire kills Opuntia spp. Some portions of stem may survive light-severity fire [3]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Mortality of fire-weakened surviving cacti may be high the first 3 postfire years. A closely related species, brownspine eastern prickly-pear (O. phaecantha), experienced high die-off following light-severity fire in Callahan County, Texas. Initial fire mortality was 20 percent. Insects entered surviving plants through fire-scarred tissue, spreading bacterial and fungal infections. New sprouts appeared within a few weeks following the fire, but many sprouting plants lost their vascular connection to the root because of insect damage and decay. By the end of the third year, mortality exceeded 70 percent. Most plants surviving through postfire year 3 had sprouted from the caudex [5]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Frequent fire reduces populations of small Opuntia species like prickly pear cactus [3].

REFERENCES

SPECIES: Opuntia humifusa | Eastern Prickly-Pear
REFERENCES : 1. Anthony, Margery. 1954. Ecology of the Opuntiae in the Big Bend region of Texas. Ecology. 35(3): 334-347. [5060] 2. Benson, Lyman. 1982. The cacti of the United States and Canada. Stanford, CA: Stanford University Press. 1044 p. [1513] 3. Benson, Lyman; Walkington, David L. 1965. The southern Californian prickly pears--invasion, adulteration, and trial-by-fire. Annals of the Missouri Botanical Garden. 52: 262-273. [5267] 4. 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] 5. Bunting, Stephen C.; Wright, Henry A.; Neuenschwander, Leon F. 1980. Long-term effects of fire on cactus in the southern mixed prairie of Texas. Journal of Range Management. 33(2): 85-88. [4271] 6. Callahan, J. L.; Barnett, C.; Cates, J. W. H. 1990. Palmetto prairie creation on phosphate-mined lands in central Florida. Restoration & Management Notes. 8(2): 94-95. [13833] 7. Cohn, Jeffrey P.; Kline, Virginia. 1982. Of prairies and prickly pears. Nature Conservancy News. 32(6): 17-22. [2814] 8. Conover, Denis G.; Geiger, Donald R. 1989. Establishment of a prairie on a borrow-pit at the Bergamo-Mt. St. John Nature Preserve in Greene County, Ohio. Ohio Journal of Science. 89(3): 42-44. [9744] 9. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 10. Fernald, Merritt Lyndon. 1950. Gray's manual of botany. [Corrections supplied by R. C. Rollins]. Portland, OR: Dioscorides Press. 1632 p. (Dudley, Theodore R., gen. ed.; Biosystematics, Floristic & Phylogeny Series; vol. 2). [14935] 11. 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. Gilmore, Melvin Randolph. 1919. Uses of plants by the Indians of the Missouri River region. 33rd Annual Report. Washington, DC: Bureau of American Ethnology. 154 p. [6928] 13. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 14. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press Inc. 666 p. [6851] 15. Humphrey, Robert R. 1960. Forage production on Arizona ranges. V. Pima, Pinal and Santa Cruz Counties. Bulletin 502. Tucson, AZ: University of Arizona, Agricultural Experiment Station. 137 p. [4520] 16. 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] 17. Kaul, Robert P.; Keeler, Kathleen H. 1980. Effects of grazing and juniper-canopy closure on the prairie flora in Nebraska high-plains canyons. In: Kucera, Clair L., ed. Proceedings, 7th North American prairie conference; 1980 August 4-6; Springfield, MO. Columbia, MO: University of Missouri: 95-105. [2923] 18. 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] 19. Lonard, Robert I.; Judd, Frank W. 1989. Phenology of native angiosperms of South Padre Island, Texas. In: Bragg, Thomas B.; Stubbendieck, James, eds. Prairie pioneers: ecology, history and culture: Proceedings, 11th North American prairie conference; 1988 August 7-11; Lincoln, NE. Lincoln, NE: University of Nebraska: 217-222. [14049] 20. 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] 21. National Academy of Sciences. 1971. Atlas of nutritional data on United States and Canadian feeds. Washington, DC: National Academy of Sciences. 772 p. [1731] 22. Olson, Jerry S. 1958. Rates of succession and soil changes on southern Lake Michigan sand dunes. Botanical Gazette. 119(3): 125-170. [10557] 23. Quinton, Dee A.; Horejsi, Ronald G. 1977. Diets of white-tailed deer on the Rolling Plains of Texas. Southwestern Naturalist. 22(4): 505-509. [12220] 24. Ramaley, Francis. 1939. Sand-hill vegetation of northeastern Colorado. Ecological Monographs. 9(1): 1-51. [5546] 25. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 26. Richardson, Donald Robert. 1977. Vegetation of the Atlantic Coastal Ridge of Palm Beach County, Florida. Florida Scientist. 40(4): 281-330. [9644] 27. Tiffney, W., Jr.; Eveleigh, D.; Barrera, J.; Mitchell, S. 1979. Evaluation of some nitrogen-fixing plants for coastal zone management applications. In: Gordon, J.C.; Wheeler, C.T.; Perry, D.A., eds. Symbiotic nitrogen fixation in the management of temperate forests: Proceedings of a workshop; 1979 April 2-5; Corvallis, OR. Corvallis, OR: Oregon State University, Forest Research Laboratory: 420-428. [4309] 28. Timmons, F. L. 1942. The dissemination of prickly pear seed by jack rabbits. Journal of the American Society of Agronomy. 34: 513-520. [5214] 29. Thornber, J.J. 1911. Native cacti as emergency forage plants. In: Bulletin No. 67. Tucson, AZ: University of Arizona, Agricultural Experiment Station: 457-508. [5089] 30. 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] 31. Committee on the Status of Endangered Wildlife in Canada. 1992. Canadian species at risk. Ottawa, ON. 10 p. [26183]

Index

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