Hostname: page-component-586b7cd67f-rcrh6 Total loading time: 0 Render date: 2024-11-22T12:30:59.501Z Has data issue: false hasContentIssue false

Aboveground Biomass of an Invasive Tree Melaleuca (Melaleuca quinquenervia) before and after Herbivory by Adventive and Introduced Natural Enemies: A Temporal Case Study in Florida

Published online by Cambridge University Press:  20 January 2017

Min B. Rayamajhi*
Affiliation:
United States Department of Agriculture, Agriculture Research Service, Invasive Plant Research Laboratory, 3225 College Ave., Fort Lauderdale, FL 33314
Paul D. Pratt
Affiliation:
United States Department of Agriculture, Agriculture Research Service, Invasive Plant Research Laboratory, 3225 College Ave., Fort Lauderdale, FL 33314
Ted D. Center
Affiliation:
United States Department of Agriculture, Agriculture Research Service, Invasive Plant Research Laboratory, 3225 College Ave., Fort Lauderdale, FL 33314
Philip W. Tipping
Affiliation:
United States Department of Agriculture, Agriculture Research Service, Invasive Plant Research Laboratory, 3225 College Ave., Fort Lauderdale, FL 33314
Thai K. Van
Affiliation:
United States Department of Agriculture, Agriculture Research Service, Invasive Plant Research Laboratory, 3225 College Ave., Fort Lauderdale, FL 33314
*
Corresponding author's E-mail: min.rayamajhi@ars.usda.gov

Abstract

Invasive plants can respond to injury from natural enemies by altering the quantity and distribution of biomass among woody materials, foliage, fruits, and seeds. Melaleuca, an Australian tree that has naturalized in south Florida, has been reunited with two natural enemies: a weevil introduced during 1997 and a psyllid introduced during 2002. We hypothesized that herbivory from these and other adventive organisms (lobate-lac scale and a leaf-rust fungus) would alter the distribution and allocation of biomass on melaleuca trees. This hypothesis was tested by temporally assessing changes in aboveground biomass components in conjunction with the presence of natural enemies and their damage to melaleuca trees. Melaleuca trees of different diameters representing the range (1 to 33 cm diam at 1.3 m height) within study sites were harvested during 1996, prior to the introduction of herbivorous insects, and again during 2003 after extensive tree damage had become apparent. Aboveground biomass, partitioned into several components (woody structures, foliage, fruits, and seeds), was quantified both times in Broward, Miami–Dade, and Palm Beach county sites located in south Florida. The two harvests within each site were performed in closely-matched melaleuca stands, and changes in biomass components were compared between years. Total biomass and woody portions decreased in Broward, whereas they increased in Miami–Dade and Palm Beach sites. Reductions in foliage (on all trees) and seed biomass (among seed-bearing trees) were greatest at Broward and least at Miami–Dade County site. Hence, overall seed and foliage production was severely reduced at the Broward site where both the natural enemy incidence and damage were more abundant compared to other sites. We therefore attribute the reduced foliar biomass and reproductive capability of melaleuca trees to infestations of natural enemies. These findings highlight the role that natural enemies can play in the long-term management of invasive tree species.

Type
Weed Management
Copyright
Copyright © Weed Science Society of America 

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

Literature Cited

Balciunas, J. K., Burrows, D. W., and Purcell, M. F. 1994. Field and laboratory host ranges of the Australian weevil, Oxyops vitiosa (Coleoptera: Curculionidae), a potential biological control agent for the paperbark tree, Melaleuca quinquenervia . Biol. Control. 4:351360.CrossRefGoogle Scholar
Binkley, D., White, C. S., and Gosz, J. R. 2004. Tree biomass and net increment in an old aspen forest in New Mexico. For. Ecol. Manag. 203:407410.Google Scholar
Bodle, M. J., Ferriter, A. P., and Thayer, D. D. 1994. The biology, distribution, and ecological consequences of Melaleuca quinquenervia in the Everglades. Pages 341355. in Davis, S. M. and Ogden, J. C. The Everglades: The Ecosystem and Its Restoration. Delray Beach, FL St. Lucie Press.Google Scholar
Brown, R. B., Stone, E. L., and Carlisle, V. W. 1991. Soils. Pages 3569. in Myers, R. L. and Ewel, J. J. Ecosystems of Florida. Orlando, FL University of Central Florida Press.Google Scholar
Center, T. D., Van, T. K., Rayachhetry, M. B., Buckingham, G. R., Dray, F. A. Jr., Wineriter, S. A., Purcell, M. F., and Pratt, P. D. 2000. Field colonization of the melaleuca snout beetle (Oxyops vitiosa) in south Florida. Biol. Control. 19:112123.Google Scholar
Chen, E. and Gerber, J. F. 1991. Climate. Pages 1134. in Myers, R. L. and Ewel, J. J. Ecosystems of Florida. Orlando, FL University of Central Florida Press.Google Scholar
Clough, B. F., Dixon, P., and Dalhaus, O. 1997. Allometric relationships for estimating biomass in multi-stemmed mangrove trees. Aust. J. Bot. 45:10231031.Google Scholar
Denslow, J. S. and D'Antonio, C. M. 2005. After biocontrol: assessing indirect effects of insect releases. Biol. Control. 35:307318.Google Scholar
Feeny, P. 1976. Plant apparency and chemical defense. Recent Adv. Phytochem. 10:140.Google Scholar
Hofstetter, R. H. 1991. The current status of Melaleuca quinquenervia in South Florida. Pages 159176. in Center, T. D., Doren, R. F., Hofstetter, R. H., Myers, R. L., and Whiteaker, L. D. Proceedings of the Symposium on Exotic Pest Plants, November 2–4, 1988. Washington DC U.S. Department of the Interior., National Park Service.Google Scholar
Kosola, K. R., Dickman, D. I., and Paul, E. A. 2001. Repeated insect defoliation effects on growth, nitrogen acquisition, carbohydrates, and root demography of poplars. Oecologia. 129:6574.Google Scholar
Kushlan, J. A. 1991. Soils. Pages 324363. in Myers, R. L. and Ewel, J. J. Ecosystems of Florida. Orlando, FL University of Central Florida Press.Google Scholar
Laundon, G. F. and Waterson, J. M. 1965. Puccinia psidii. C.M.I. Description of Pathogenic Fungi and Bacteria. No. 56. Kew, Surrey, England, United Kingdom Commonwealth Mycological Institute.Google Scholar
Marlatt, R. B. and Kimbrough, J. W. 1979. Puccinia psidii on Pimenta dioica in south Florida. Plant Dis. Rep. 63:510512.Google Scholar
Meskimen, G. F. 1962. A silvical study of the melaleuca tree in south Florida. . Gainesville, FL University of Florida. 177.Google Scholar
Morath, S., Pratt, P. D., Silvers, C. S., and Center, T. D. 2006. Herbivory by Boreioglycaspis melaleucae (Hemiptera: Psyllidae) accelerates foliar degradation and abscission in the invasive tree Melaleuca quinquenervia . Environ. Entomol. 35:13721378.Google Scholar
Nemeth, J. C. 1973. Dry matter production in young loblolly (Pinus taeda L.) and slash (Pinus elliotii Engelm.) pine plantations. Ecol. Monogr. 43:2141.Google Scholar
Parker, J. and Patton, R. L. 1975. Effects of drought and defoliation on some metabolites in roots of black oak seedlings. Can. J. For. Res. 5:457463.CrossRefGoogle Scholar
Pemberton, R. W. 2003. Invasion of Paratachardina lobata lobata (Hemiptera: Kerriidae) in south Florida. Fla. Entomol. 86:373377.Google Scholar
Pratt, P. D., Rayamajhi, M. B., Van, T. K., and Center, T. D. 2005. Herbivory alters resource allocation and compensation in the invasive tree Melaleuca quinquenervia . Ecol. Entomol. 15:443462.Google Scholar
Rayachhetry, M. B., Elliot, M. L., and Van, T. K. 1997. Natural epiphytotic of a rust fungus (Puccinia psidii) on Melaleuca quinquenervia in Florida. Plant Dis. 81:831.Google Scholar
Rayachhetry, M. B., Van, T. K., and Center, T. D. 1998. Regeneration potential of the canopy-held seeds of Melaleuca quinquenervia in Florida. Int. J. Plant Sci. 159:648654.CrossRefGoogle Scholar
Rayachhetry, M. B., Van, T. K., Center, T. D., and Elliott, M. L. 2001a. Host range of Puccinia psidii, a potential biological control agent of Melaleuca quinquenervia in Florida. Biol. Control. 22:3845.Google Scholar
Rayachhetry, M. B., Van, T. K., Center, T. D., and Laroche, F. B. 2001b. Dry weight estimation of the above-ground components of Melaleuca quinquenervia trees in southern Florida. For. Ecol. Manag. 142:281290.Google Scholar
Rayamajhi, M. B., Van, T. K., Pratt, P. D., and Center, T. D. 2006. Temporal and structural effects of stands on litter production in Melaleuca quinquenervia dominated wetlands of south Florida. Wetl. Ecol. Manag. 14:303316.Google Scholar
Rayamajhi, M. B., Van, T. K., Pratt, P. D., Center, T. D., and Tipping, P. W. 2007. Melaleuca quinquenervia dominated forests in Florida: analyses of natural-enemy impacts on stand dynamics. Plant Ecol. 192:119132.Google Scholar
SAS 1999. SAS, Version 8. Cary, NC SAS Institute Inc. 3884.Google Scholar
Schowalter, T. D. 2000. Insect Ecology. San Diego, CA Academic Press. 576.Google Scholar
Sokal, R. R. and Rohlf, F. J. 1981. Biometry. New York W. H. Free man. 859.Google Scholar
Van, T. K., Rayamajhi, M. B., and Center, T. D. 2000. Estimating above-ground biomass of Melaleuca quinquenervia in Florida, USA. J. Aquat. Plant Manag. 38:6267.Google Scholar
Wargo, P. M. 1972. Defoliation-induced chemical changes in sugar maple roots stimulate growth of Armillaria melia . Phytopathol. 62:12781283.Google Scholar
Wargo, P. M., Parker, J., and Houston, D. R. 1972. Starch content in roots of defoliated sugar maple. For. Sci. 18:203204.Google Scholar
Waring, R. H. and Pitman, G. B. 1980. A simple model of host resistance to bark beetles. Forest Research Laboratory. Research Note 65. Corvallis, OR School of Forestry, Oregon State University. 8.Google Scholar
Woodall, S. L. 1982. Seed dispersal in Melaleuca quinquenervia . Fla. Sci. 46:6571.Google Scholar