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Introductory

SPECIES: Schinus terebinthifolius | Brazilian Pepper
ABBREVIATION : SCHTER SYNONYMS : NO-ENTRY SCS PLANT CODE : SCTE COMMON NAMES : Brazilian pepper Christmas-berry Florida holly aroeira TAXONOMY : The currently accepted scientific name for Brazilian pepper is Schinus terebinthifolius Raddi [34]. There are no recognized subspecies, varieties, or forms. LIFE FORM : Tree, Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Milo Coladonato, October 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Coladonato, Milo. 1992. Schinus terebinthifolius. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Schinus terebinthifolius | Brazilian Pepper
GENERAL DISTRIBUTION : Brazilian pepper is indigenous to the coast of tropical Brazil. It has been introduced to several countries in South America, parts of Central America, Bermuda, the Bahamas, and the west Indies. In the continental United States, Brazilian pepper is naturalized on a significant scale only in southern Florida. Brazilian pepper has also been introduced in Hawaii, California, and Texas [15,25]. ECOSYSTEMS : FRES12 Longleaf - slash pine FRES14 Oak - pine FRES16 Oak - gum - cypress STATES : CA FL HI TX ADMINISTRATIVE UNITS : BICY BISC EVER HALE HAVO VIIS BLM PHYSIOGRAPHIC REGIONS : NO-ENTRY KUCHLER PLANT ASSOCIATIONS : K079 Palmetto prairie K090 Live oak - sea oats K091 Cypress savanna K092 Everglades K105 Mangrove K112 Southern mixed forest K115 Sand pine scrub K116 Subtropical pine forest SAF COVER TYPES : 72 Southern scrub oak 74 Cabbage palmetto 83 Longleaf pine - slash pine 100 Pondcypress 101 Baldcypress 102 Baldcypress - tupelo 103 Water tupelo - swamp tupelo SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : NO-ENTRY

VALUE AND USE

SPECIES: Schinus terebinthifolius | Brazilian Pepper
WOOD PRODUCTS VALUE : The wood of Brazilian pepper is used in construction, as stakes, posts, and railway sleepers. The twigs are also made into toothpicks [3,22]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : The fruit of Brazilian pepper is readily eaten by wildlife, but the seed pass through the digestive tract unharmed [32]. The unripe fruit if ingested can be fatal to horses, and the ripe fruit causes intoxication in birds if eaten in large quantities [3]. PALATABILITY : NO-ENTRY NUTRITIONAL VALUE : NO-ENTRY COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : Because of its fast growth and ability to quickly invade disturbed sites, Brazilian pepper can be planted for erosion control on deforested sites. However, it is not recommended for this use because of its deleterious effects on native plant and animal species [6]. OTHER USES AND VALUES : Brazilian pepper serves as a source of tannin, and the resinous extracts are used to preserve fishing nets. It is grown as an ornamental in Brazil. Medicinal uses include a remedy for gout, arthitic pain, and diarrhea [2,3]. The juice of the macerated roots is used as an ointment for ganglionic tumors and contusions [22]. In Hawaii, the bright red berries are used in making Christmas wreaths; hence the name Christmas- berry [33]. Brazilian pepper has been planted as an ornamental in Florida and Hawaii but is no longer recommended for this use [21]. MANAGEMENT CONSIDERATIONS : Among the negative effects of the steady expansion of Brazilian pepper in south Florida is the elimination of native plant species and sources of food for native wildlife. Originally planted as an ornamental it has spread across hundreds of square kilometers and become a formidable competitor for water and mineral resources [5,17]. Brazilian pepper also produces an allelopathic chemical in its leaves that suppresses the growth of other plants [22,26]. In Hawaii, Brazilian pepper is having a harmful impact on many endangered and threatened species, including the Haleakala silverword (Argyroxiphium sandwicense spp. macrocephalum), liliwai (Acaena exigua), and the mahoe tree (Alectryon macrococcus) [30]. The most effective method of controlling Brazilian pepper is to fetter out individuals that colonize naturally occuring gaps and by burning pine forest regularly, although this method will not eliminate Brazilian pepper from the site [10]. The methods and effectiveness of various herbicide treatments of Brazilian pepper have been outlined [8,17].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Schinus terebinthifolius | Brazilian Pepper
GENERAL BOTANICAL CHARACTERISTICS : Brazilian pepper is a thicket-forming, medium-sized large shrub or small exotic tree to 40 feet (12 m) high. Its short trunk is about 3 feet (1 m) thick, usually hidden by a dense head of contorted intertwining branches, drooping at the tips, and heavily clothed with evergreen pinnate foliage. The oblong or elliptical leaves have 3 to 13 sessile, resinous leaflets about 1 to 2 inches (2.5-5 cm) long. The white flowers are five-petaled and are borne on the axils of the leaflets along the outer 3 feet (1 m) of the branches and at the branch tips. Some specimens bear only male flowers. The fruit is a red, resinous one-seeded berry [22]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Brazilian pepper's primary mode of reproduction is sexual. It produces an abundance of large seeds, particularly after fire or mechanical disturbance. The seeds are dispersed by many mammals and birds including mockingbirds, cedar waxwings, and especially migrating robins [10,22]. Bazilian pepper also has the ability to sprout from adventitious buds on its roots or shoots [13,17]. SITE CHARACTERISTICS : Brazilian pepper grows on a broad range of sites in South Florida, ranging from mangroves to pinelands. It thrives on disturbed soils and in newly created habitats resulting from drainage and farming. It grows best on well-drained wastelands and abandoned oldfields [4,10]. Some common associates of Brazilian pepper not listed in SAF include buttonbush (Cephalanthas occidentalis), water ash (Fraxinus carolina), water hickory (Carya acquatica), hackberry (Celtis laevigata), redbay (Persea borbonia), melaleuca (Melaleuca quinquenervia), cabbage palmetto (Sabal palmetto), southern bayberry (Myrica cerifera), saw palmetto (Sereroa repens), swamp bay (Persea palustris), Australian pine (Casuarina equisetifolia), and coco plum (Chrysobalanus icaco) [9,11,19,24,31]. SUCCESSIONAL STATUS : Obligate Initial Community Species Brazilian pepper is an early invader of disturbed sites [1,28]. Its behavior is analogous to a "sit-and-wait predator", becoming established in the understory of dense forests, then capturing the site when gaps occur in the canopy [10]. Brazilian pepper has a relatively high tolerance for shade. The seedlings appear to be barely surviving in dense shade but will quickly respond to altered environmental conditions. Brazilian pepper is a potential canopy tree in almost any forest in South Florida [10,20]. SEASONAL DEVELOPMENT : Brazilian pepper flowers synchronously in October and is pollinated by a native syrphid fly. Its fruit ripens in December through February and its leaves are produced throughout the year [10,13].

FIRE ECOLOGY

SPECIES: Schinus terebinthifolius | Brazilian Pepper
FIRE ECOLOGY OR ADAPTATIONS : Brazilian pepper forms dense thickets that fire rarely penetrates. It produces new leaves throughtout the year and because its litter decomposes quickly, very little leaf litter builds up on the forest floor. The high moisture content of the leaves and wood also make it difficult to burn. When Brazilian pepper does burn (as it frequently does when it colonizes open pinelands), the aboveground parts are killed, but the the tree promptly sprouts from the base [10]. Brazilian pepper is also able to reestablish after fire from seed dispersed from adjacent sites or stored on-site in the seed bank [7,27]. POSTFIRE REGENERATION STRATEGY : Tree with adventitious-bud root crown/root sucker Secondary colonizer - on-site seed Secondary colonizer - off-site seed

FIRE EFFECTS

SPECIES: Schinus terebinthifolius | Brazilian Pepper
IMMEDIATE FIRE EFFECT ON PLANT : Fire effects on Brazilian pepper are related to the size of the seedling, amount of available fuel around the plant, and fire severity. Smaller, recently established plants are severly retarded in growth or killed from moderate and severe fires. Larger plants are only top-killed or do not burn at all due to the fact that the fires are not always able to penetrate the dense thickets [6]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Brazilian pepper is able to regenerate after fire by sprouting from the root or root collar resulting in more stem production than was the case prior to the burn [17]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Although fire will kill some Brazilian pepper seedlings, it is not recommended as an effective control of this species once it has formed dense thickets. In fact, hedgerows of Brazilian pepper are often used as fire breaks [32]. Even repeated burnings will not prevent the invasion of Brazilian pepper into large disturbed areas [6].

REFERENCES

SPECIES: Schinus terebinthifolius | Brazilian Pepper
REFERENCES : 1. Austin, Daniel F. 1976. Vegetation of southeastern Florida--I. Pine Jog. Florida Scientist. 39(4): 230-235. [14570] 2. Balciunas, Joseph K.; Center, Ted D. 1991. Biological control of Melaleuca quinquenervia: prospects and conflicts. In: Center, Ted D.; Doren, Robert F.; Hofstetter, Ronald L.; [and others], eds. Proceedings of the symposium on exotic pest plants; 1988 November 2-4; Miami, FL. Tech. Rep. NPS/NREVER/NRTR-91/06. Washington, DC: U.S. Department of the Interior, National Park Service: 1-22. [17855] 3. Bennett, Fred D.; Habeck, Dale H. 1991. Brazilian peppertree - prospects for biological control in Florida. In: Center, Ted D.; Doren, Robert F.; Hofstetter, Ronald L.; Myers, Ronald L.; Whiteaker, Louis D, eds. Proceedings of the Symposium on Exotic Pest Plants; 1988 November 2 - November 4; Miami, FL. Tech. Rep. NPS/NREVER/NRTR-91/06. Washington, DC: U.S. Department of the Interior, National Park Service: 23-33. [17856] 4. Christopher, Sandy; Kampert, Elliot L. 1992. Brazilian pepper bombs. Arbor Age. 12(4): 22. [18131] 5. DeLoach, C. Jack. 1991. Past successes and current prospects in biological control of weeds in the United States and Canada. Natural Areas Journal. 11(3): 129-142. [15248] 6. Doren, Robert F.; Whiteaker, Louis D. 1990. Effects of fire on different size individuals of Schinus terebinthifolius. Natural Areas Journal. 10(3): 107-113. [16966] 7. Doren, Robert F.; Whiteaker, Louis D.; La Rosa, Anne Marie. 1991. Eval. of fire as a mgmt tool for controlling Schinus terebinthifolius as secondary successional growth on abandoned agricultural land. Environmental Management. 15(1): 121-129. [14594] 8. Doren, Robert F.; Whiteaker, Louis D.; Rochefort, Regina. 1991. Seasonal effects on herbicide basal bark treatment of Schinus terebinthifolius. In: Center, Ted D.; Doren, Robert F.; Hofstetter, Ronald L.; [and others]., eds. Proceedings of the symposium on exotic pest plants; 1988 November 2-4; Miami, FL. Tech. Rep. NPS/NREVER/NRTR-91/06. Washington, DC: U.S. Department of the Interior, National Park Service: 115-129. [17861] 9. Duever, Michael J.; Meeder, John F.; Duever, Linda C. 1984. Ecosystems of the big cypress swamp. In: Ewel, Katherine Carter; Odum, Howard T., eds. Cypress swamps. Gainesville, FL: University of Florida Press: 294-303. [14853] 10. Ewel, J. J. 1986. Invasibility: Lessons from south Florida. In: Mooney, Harold A.; Drake, James A., eds. Ecology of biological invasions of North America and Hawaii. Ecological Studies 58. New York: Springer-Verlag: 214-230. [17517] 11. Ewel, Katherine Carter. 1984. Effects of fire and wastewater on understory vegetation in cypress domes. In: Ewel, Katherine Carter; Odum, Howard T., eds. Cypress swamps. Gainesville, FL: University of Florida Press: 119-126. [14845] 12. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 13. Fernald, Raymond T.; Barnett, Brian S. 1991. Establishment of native hammock vegetation on spoil islands dominated by Australian pine (Casuarina equisetifolia) & Brazilian pepper. In: Center, Ted D.; Doren, Robert F.; Hofstetter, Ronald L.; [and others], eds. Proceedings of the symposium on exotic pest plants; 1988 November 2-4; Miami, FL. Tech. Rep. NPS/NREVER/NRTR-91/06. Washington, DC: U.S. Department of the Interior, National Park Service: 131-150. [17862] 14. 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] 15. Godfrey, Robert K.; Wooten, Jean W. 1981. Aquatic and wetland plants of southeastern United States: Dicotyledons. Athens, GA: The University of Georgia Press. 933 p. [16907] 16. 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] 17. Langeland, Ken, editor. 1990. Exotic woody plant control. Circular 868. Gainsville, FL: University of Florida, Cooperative Extension Service, Institute of Food and Agricultural Sciences. 16 p. [17344] 18. Little, Elbert L., Jr. 1979. Checklist of United States trees (native and naturalized). Agric. Handb. 541. Washington, DC: U.S. Department of Agriculture, Forest Service. 375 p. [2952] 19. Long, Robert W. 1974. The vegetation of southern Florida. Florida Scientist. 37(1): 33-45. [9151] 20. Loope, Lloyd L.; Dunevitz, Vicki L. 1981. Impact of fire exclusion and invasion of Schinus terebinthifolius on limestone rockland pine forests of southeastern Florida. Report T-645. Homestead, FL: U.S. Department of the Interior, South Florida Research Center, Everglades National Park. 30 p. [17457] 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. Morton, Julia F. 1978. Brazilian pepper - its impact on people, animals and the environment. Economic Botany. 32(4): 353-359. [17726] 23. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 24. Richardson, Donald Robert. 1977. Vegetation of the Atlantic Coastal Ridge of Palm Beach County, Florida. Florida Scientist. 40(4): 281-330. [9644] 25. Schmitz, Don C.; Nelson, Brian V.; Nall, Larry E.; Schardt, Jeffrey D. 1991. Exotic aquatic plants in Florida: A historical perspective and review of the present aquatic plant regulation program. In: Center, Ted D.; Doren, Robert F.; Hofstetter, Ronald L.; [and others], eds. Proceedings of the symposium on exotic pest plants; 1988 November 2-4; Miami, FL. Tech. Rep. NPS/NREVER/NRTR-91/06. Washington, DC: U.S. Department of the Interior, National Park Service: 303-326. [17873] 26. Smith, Clifford W. 1991. The alien plant problem in Hawaii. In: Center, Ted D.; Doren, Robert F.; Hofstetter, Ronald L.; [and others], eds. Proceedings of the symposium on exotic pest plants; 1988 November 2-4; Miami, FL. Tech. Rep. NPS/NREVER/NRTR-91/06. Washington, DC: U.S. Department of the Interior, National Park Service: 327-338. [17874] 27. Taylor, Dale L. 1980. Fire history and man-induced fire problems in subtropical south Florida. In: Stokes, Marvin A.; Dieterich, John H., technical coordinators. Proceedings of the fire history workshop; 1980 October 20-24; Tucson, AZ. Gen. Tech. Rep. RM-81. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 63-68. [16044] 28. Taylor, Dale L.; Herndon, Alan. 1981. Impact of 22 years of fire on understory hardwood shrubs in slash pine communities within Everglades National Park. Report T-640. Homestead, FL: National Park Service, South Florida Research Center, Everglades National Park. 30 p. [11961] 29. 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] 30. U.S. Department of the Interior, Fish and Wildlife Service. 1991. Fifteen Hawaiian plants proposed in May for Endangered Species Act protection. Endangered Species Technical Bulletin. 16(6): 1, 5-7. [16517] 31. Wade, Dale D.; Langdon, O. Gordon. 1990. Sabal palmetto (Walt.) Lodd. ex J. A. & J. H. Schult. cabbage palmetto. In: Burns, Russell M.; Honkala, Barbara H., technical coordinators. Silvics of North America. Vol. 2. Hardwoods. Agric. Handb. 654. Washington, DC: U.S. Department of Agriculture, Forest Service: 762-767. [13806] 32. Wade, Dale; Ewel, John; Hofstetter, Ronald. 1980. Fire in south Florida ecosystems. Gen. Tech. Rep. SE-17. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station. 125 p. [10363] 33. Yoshioka, E. R.; Markin, G. P. 1991. Efforts of biological control of Christmas berry (Schinus terebinthifolia) in Hawaii. In: Center, Ted D.; Doren, Robert F.; Hofstetter, Ronald L.; [and others]., eds. Proceedings of the symposium on exotic pest plants; 1988 November 2-4; Miami, FL. Tech. Rep. NPS/NREVER/NRTR-91/06. Washington, DC: U.S. Department of the Interior, National Park Service: 377-387. [17877] 34. Wunderlin, Richard P. 1982. Guide to the vascular plants of central Florida. Tampa, FL: University Presses of Florida, University of South Florida. 472 p. [13125]

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