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Introductory

SPECIES: Melaleuca quinquenervia | Melaleuca
ABBREVIATION : MELQUI SYNONYMS : NO-ENTRY SCS PLANT CODE : MEQU COMMON NAMES : melaleuca cajeput punk-tree paper-bark tree five-veined paperbark bottle-brush tree TAXONOMY : The currently accepted scientific name for melaleuca is Melaleuca quinquenervia (Cav.) S. T. Blake [13]. There are no recognized subspecies, varieties, or forms. LIFE FORM : Tree FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Milo Coladonato, September 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Coladonato, Milo. 1992. Melaleuca quinquenervia. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Melaleuca quinquenervia | Melaleuca
GENERAL DISTRIBUTION : Melaleuca's native range is along the coast of eastern Australia from Sydney northward. It is native also in New Caledonia, Papua New Guinea, and Irian Jaya [8]. In the continental United States, melaleuca is naturalized on a significant scale only in southern Florida, with the largest concentrations in Palm Beach, Broward, Dade, Collier, and Glades counties [16]. A million trees have been planted in Hawaii, but natural regeneration is limited to the island of Maui. Planted melaleuca can be found in parts of southern California and southern Texas [8]. ECOSYSTEMS : FRES12 Longleaf - slash pine FRES15 Oak - hickory FRES16 Oak - gum - cypress STATES : CA FL HI TX ADMINISTRATIVE UNITS : BICY EVER HALE BLM PHYSIOGRAPHIC REGIONS : KUCHLER PLANT ASSOCIATIONS : K079 Palmetto prairie K091 Cypress savanna K092 Everglades K112 Southern mixed forest K115 Sand pine scrub SAF COVER TYPES : 70 Longleaf pine 83 Longleaf pine - slash pine 84 Slash pine 100 Pondcypress 101 Baldcypress 111 South Florida slash pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : NO-ENTRY

VALUE AND USE

SPECIES: Melaleuca quinquenervia | Melaleuca
WOOD PRODUCTS VALUE : Melaleuca is not used in Florida or Hawaii for commercial lumber because its bark-to-wood ratio is high, the average stem diameter small, and the form poor. However, the wood is suitable for uses such as pulp and cabinetry. The wood can be used for fuel but is more difficult to use than other species because of its powdery, low-density bark [8]. Experimental work has been done on melaleuca for production of sawwood, gunstocks, cutting boards, trophy plaques, furniture, and fence posts. The results of these tests have been satisfatory to excellent. The species may be undesirable for tomato stakes because of the allelopathic resins in the wood [3]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : Melaleuca provides little food for wildlife, and dense young stands have been labeled "particularly poor wildlife habitat." Studies in southern Florida indicate that while 10 percent of birds active in melaleuca heads actually feed there, only 1.5 percent nest there [3]. In south Florida melaleuca is replacing the natural habitat and food sources of native species such as alligator and deer. No small birds or mammals eat the seed of melaleuca [10]. 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, melaleuca has been planted for erosion control on deforested sites. However, it is not recommended for this use because of its deleterious effect on the habitat of native species [3,9]. OTHER USES AND VALUES : The leaves, twigs, and seeds of melaleuca produce cajeput oil that has been used as an antiseptic and analgesic. The oil has also been used in perfumes, cough drops, and as a flavoring for candy, ice cream, and beverages [3]. Melaleuca is a good source of nectar for honey, package bees, and wax. The honey, called "punk honey", is not used as table honey but is used in the baking industry [3]. Although melaleuca was originally introduced into Florida as an ornamental, it is no longer planted for this purpose [2]. MANAGEMENT CONSIDERATIONS : The spread of melaleuca has caused considerable alarm about possible irreversible changes that may be occurring in the ecosystem of south Florida. Originally planted as an ornamental, it has spread across hundreds of square kilometers and has become a formidable competitor for water and mineral resources. It also has the potential to replace hundreds of local plants and moderately or severely impact several animal species, some of which are endangered or threatened [20]. Mechanical removal: Mechanical clearing with a follow-up seedling control program is an effective but expensive long-term solution. If cleared lands receive no on-going mechanical treatment, melaleuca will invade and rapidly colonize the disturbed soil. Downed trees and limbs should be removed from the site to eliminate the seed source and potential sprouting [15]. Herbicides: Most herbicides show limited effectiveness against melaleuca. Most provide only short-term results, and melaleuca trees quickly refoliate after treatment. Some of the more effective uses of herbicides under various conditions have been outlined [4,12]. Biological control: Research is currently being done in the use of various biological controls of melaleuca. Workers in Australia have identified more than 50 species of insects that utilize melaleuca as a food source. Long-term control of melaeuca would best be achieved with the introduction of effective biological control agents. However, the prospect of biological agents solving the problem of melaleuca within the next decade is remote [20].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Melaleuca quinquenervia | Melaleuca
GENERAL BOTANICAL CHARACTERISTICS : Melaleuca is a relatively fast-growing evergreen tree reaching a height of about 90 feet (27 m), but more commonly 50 to 70 feet (15-21 m). It grows in typically dense monocultures. It is self-pruning, tall and slender, and generally lacks branches on the lower two-thirds of its bole. The branches are slender and moderately short. Trees grown in the open have a broader, columnar form with dense branches extending from near the soil surface to the top of the tree. Some have multiple trunks, often more than a dozen that originate close to the soil surface and diverge outward, giving it a shrublike form. The white flowers are borne on spikes with an average of 30 sessile capsules per flower spike. A branch may bear 8 to 12 of these seed-bearing sections, often alternating with foliage, along a single axis. The hard, woody capsules are aggregated along the branches. The thick, low-density bark contains multiple layers of paperlike material that retains both considerable moisture and abundant small air spaces. The leaves are simple and arranged in five spiral rows. The root system of melaleuca is adapted to fluctuating water tables. The surface root network is characterized by abundant vertical sinker roots that extend at least to the water table's deepest annual level. During periods of surface flooding, "water roots" proliferate from permanent surface roots and submerged portions of the stems [8,9,12]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Seed production and dissemination: Melaleuca's primary mode of reproduction is sexual. It produces an abundance of small, lightweight seeds and can begin seed production as early as 1 year of age, although most trees do not flower that young. Viable seeds are present in capsules that are 15 years old, but viability of seeds declines with age. Some capsules apparently open constantly, releasing a continous light rain of seeds. Most capsules are serotinous. They do not open until the conductive tissue connecting them to the tree is disrupted by shoot growth and bark production, or by stress, such as fire, frost, mechanical damage, or herbicide treatment. Following stress, a massive seed release may begin within a few hours and occur over several days. Melaleuca has no adaptations that aid in seed dispersal. The seed is not dispersed by any native birds or mammals. Most seeds fall close to the parent tree, with wind dispersal affected by the height of the seed release and wind speed. The seeds will also float on water if the surface tension is maintained. In spite of the small size, the seeds are surprisingly long-lived, remaining viable up to 10 months. When submerged in water, the seeds will live up to 6 months. [5,8,10] Seedling development: Germination is epigeal. Dense reproduction occurs when trees shed millions of seeds. Seedlings averaging 6.5 feet (2.0 m) tall may be as dense as 1.4 million per acre (3.5 million/ha). If seedlings are submerged by water for several months, they may survive and resume growth. Seedling growth may occur every month of the year, but growth is most rapid from spring to early fall. Natural seedlings can grow more than 3 feet (1 m) tall during the first year, while seedlings planted at a density of 4,050 per acre (10,000/ha) on drained muck soils grew 6.5 feet (2.0 m) in 6 months [8]. Vegetative reproduction: Melaleuca stumps sprout readily. The tree has the ability to generate adventitious buds on its roots and shoots. This characteristic results in coppicing below a cut or when the apical bud is destroyed. A tree that is uprooted and on the ground may develop into a row of trees as a result of branches on the upper side of the bole becoming individual trunks. Broken branches that fall on suitable soils may root and grow. The adventitious buds generate a collar of "water roots" in the water column above the sediment where there is prolonged flooding [10]. SITE CHARACTERISTICS : Melaleuca tolerates a broad range of site conditions. It becomes established more readily on sand than on marl but can survive on almost any soil in south Florida. It tolerates extended flooding, moderate drought, and some salinity [5,24]. Soils supporting melaleuca include the suborders Psammaquents, Aquods, and Saprists of the orders Entisols, Spodosols, and Histosols, respectively. Many of these soils are shallow and underlain by limestone [8]. In Hawaii, melaleuca is found from sea level to 4,500 feet (1,400 m). In grows fairly well on Hawaiian soils, especially on Inceptisols, Ultisols, and Oxisols developed on basalt ash or lava rock of pH 4.5 to 5.5 [1,8]. Some common associates of melaleuca not previously listed in Distribution and Occurrence include cabbage palmetto (Sabal palmetto), Brazilian peppertree (Schinus terebinthifolia), southern bayberry (Myrica cerifera), cocoa plum (Chrysobalanus icaco), and buttonbush (Cephalanthus occidentalis) [1,8]. SUCCESSIONAL STATUS : Obligate Initial Community Species. Melaleuca rarely has to compete directly with other tree species in Florida because it mainly invades sparsely vegetated ecotones, prairies, marshes, and fire-damaged forests. Mature trees are classed as intolerant, although some germination and seedling development does occur in shade. Massive seed release typically follows disturbance such as fire, allowing melaleuca to invade the site and form an almost pure stand. Pure stands with a closed canopy will inhibit the development of understory vegetation, including melaleuca seedlings [8,16]. SEASONAL DEVELOPMENT : Flowering occurs in every month except February, March, and April. After flowering, twigs continue to elongate from the ends of spikes to produce leaves or more flowers. Individual trees bloom from two to five times a year. In Hawaii melaleuca flowers throughout the year [8].

FIRE ECOLOGY

SPECIES: Melaleuca quinquenervia | Melaleuca
FIRE ECOLOGY OR ADAPTATIONS : Melaleuca is well adapted to fire. It has a thick, spongy bark that insulates the cambium. The outer layers of bark are flakey and burn vigorously, which conducts the fire into the canopy, igniting the oil-laden foliage. The leaves and small branches are killed, but dormant lateral buds on the trunk germinate within weeks after the burn. This prolific sprouting increases the surface area of small branches and therefore the tree's reproductive potential [5,23]. Melaleuca can flower within weeks after a fire. Each serotinous capsule contains about 250 tiny seeds which are released after a burn, frost, or any other event that severs the vascular connections to the fruit. A burned melaleuca tree can release millions of seeds, which are dispersed a short distance by wind and water [5,10]. POSTFIRE REGENERATION STRATEGY : Secondary colonizer - on-site seed Secondary colonizer - off-site seed Tree with adventitious-bud root crown/root sucker

FIRE EFFECTS

SPECIES: Melaleuca quinquenervia | Melaleuca
IMMEDIATE FIRE EFFECT ON PLANT : Seedlings that are less than 3 to 6 months old, or only 4 to 8 inches (10-20 cm) high are often killed by hot surface fires. Death may occur as a result of lethal temperatures, insufficient food reserves to produce new shoots, or drying of the sediments due to increased exposure. Older seedlings are top-killed by most fires but recover quickly, often with multiple shoots sprouting from the root collar [10]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : A mature maleleuca tree will respond to fire by releasing millions of seeds that are held in the capsules on the twigs and branches. Adults damaged by fire may also sprout vigorously from the roots, bole, or branches. The proliferation of branches on a burned adult tree often results in more twigs, and thus more capsules and more seed production than was the case prior to the burn [22,23]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Fire alone has not been recommended as an effective means of controlling melaleuca [18,19]. However, there is a possibility (as yet untried) that fire may be useful in controlling melaleuca on some sites. If the adult melaleuca were killed by below-freezing temperatures, fire might be a good method of eliminating any subsequent seedlings. A second possible use of fire would be to induce a melaleuca seed release at a time when germinating seeds would be killed by drought or flooding. This approach would require accurate predictions of water level changes and merits additional research before definite recommendations can be made [23].

REFERENCES

SPECIES: Melaleuca quinquenervia | Melaleuca
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. Diamond, Craig; Davis, Darrell; Schmitz, Don C. 1991. Economic impact statement: The addition of Melaleuca quinquenervia to the Florida prohibited aquatic plant list. 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: 87-110. [17860] 4. Doren, Robert F.; Whiteaker, Louis D. 1991. The Exotic Pest Plant Council. Restoration & Management Notes. 9(1): 29-31. [15413] 5. 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] 6. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 7. 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] 8. Geary, T. F.; Woodall, S. L. 1990. Melaleuca quinquenervia (Cav.) S. T. Blake melaleuca. In: Burns, Russell M.; Honkala, Barbara H., tech. coords. Silvics of North America. Vol. 2. Hardwoods. Agric. Handb. 654. Washington, DC: U.S. Department of Agriculture, Forest Service: 461-465. [18955] 9. 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] 10. Hofstetter, Ronald H. 1991. The current status of Melaleuca quinquenervia in southern Florida. 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: 159-176. [17864] 11. 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] 12. 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] 13. 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] 14. 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] 15. Maffei, Mark D. 1991. Melaleuca control on Arthur R. Marshall Loxahatchee National Wildlife Refuge. 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: 197-207. [17867] 16. Myers, Ronald L. 1984. Ecological compression of Taxodium distichum var. nutans by Melaleuca quinquenervia in Florida. In: Ewel, Katherine Carter; Odum, Howard T., eds. Cypress swamps. Gainesville, FL: University of Florida Press: 358-364. [14858] 17. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 18. Snyder, James R. 1991. Fire regimes in subtropical south Florida. In: High-intensity fire in wildlands: management challenges and options: Proceedings, 17th annual meeting of the Tall Timbers fire ecology conference; 1991 May 18-21; Tallahassee, FL. Tallahassee, FL: Tall Timbers Research Station: 303-319. [17068] 19. 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] 20. Timmer, C. Elroy; Teague, Stanley S. 1991. Melaleuca eradication program: Assessment of methodology and efficacy. 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: 339-351. [17875] 21. 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] 22. Wade, Dale D. 1986. Linking fire behavior to its effects on living plant tissue. In: Proceedings of the 1986 Society of American Foresters National Convention; 1986 October 5-8; Birmingham, AL. Bethesda, MD: Society of American Foresters: 112-116. [11932] 23. 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] 24. Woodall, Steven L. 1983. Establishmentof Melaleuca quinquenervia seedlings in the pine-cypress ecotone of southwest Florida. Florida Scientist. 46(2): 65-72. [14614]

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