Hostname: page-component-586b7cd67f-l7hp2 Total loading time: 0 Render date: 2024-11-26T03:12:13.693Z Has data issue: false hasContentIssue false
  • English
  • Français

Introduction History Influences Aboveground Biomass Allocation in Brazilian Peppertree (Schinus terebinthifolius)

Published online by Cambridge University Press:  18 September 2017

Kelley D. Erickson ,
Paul D. Pratt ,
Min B. Rayamajhi  and
Carol C. Horvitz
Kelley D. Erickson*
Affiliation:
Graduate Student and Professor, Department of Biology, University of Miami, Coral Gables, FL 33146
Paul D. Pratt
Affiliation:
Research Leader, Exotic and Invasive Weeds Research Unit, United States Department of Agriculture - Agricultural Research Service (USDA-ARS), Western Regional Research Center, 800 Buchanan Street, Albany, CA 94710
Min B. Rayamajhi
Affiliation:
Research Plant Pathologist, Invasive Weed Pathology & Ecology, USDA-ARS, Invasive Plant Research Laboratory, 3225 College Avenue, Fort Lauderdale, FL 33134
Carol C. Horvitz
Affiliation:
Graduate Student and Professor, Department of Biology, University of Miami, Coral Gables, FL 33146
*
*Corresponding author’s E-mail: [email protected]
Get access Rights & Permissions [Opens in a new window]

Abstract

Multiple introductions of an exotic species can facilitate invasion success by allowing for a wider range of expressed trait values in the adventive range. Schinus terebinthifolius (Brazilian peppertree) is an invasive shrub that was introduced into Florida in two separate introductions and has subsequently hybridized, resulting in three distinct lineages (eastern, western, and hybrid). To determine whether allocation of aboveground biomass differed by introduction history, we destructively sampled 257 stems from each of six populations with differing introduction histories. The proportion of aboveground biomass allocated to fruit, wood, and leaves differed among the three populations. To determine whether the relationship between stem size and several dependent variables that measure plant performance (total dry weight, wood dry weight, number of fruits, fruit dry weight, leaf dry weight, and number of leaves) differed quantitatively by introduction history, we performed analyses of covariance. Slopes of these relationships (dependent variable vs. stem size) varied by lineage. Hybrid populations had the steepest slopes for one set of dependent variables (total dry weight, wood dry weight, and leaf dry weight), while western populations had the steepest slopes for a different set of dependent variables (number of fruits, fruit dry weight, and number of leaves). The parameterized regression equations for each dependent variable and lineage were used to nondestructively estimate different kinds of production by individuals that are part of long-term longitudinal studies to understand the demographic consequences of these different biomass allocation strategies for the performance of S. terebinthifolius individuals across the invaded range in Florida.

Keywords

Brazilian peppertreeSchinus terebinthifolius RaddiAllometryFloridahaplotypehybrid vigorinvasion
Type
Research and Education
Information
Invasive Plant Science and Management , Volume 10 , Issue 3 , September 2017 , pp. 247 - 253
Copyright
© Weed Science Society of America, 2017 

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.)

Footnotes

Associate Editor for this paper: Jacob N. Barney, Virginia Tech.

References

Literature Cited

Allendorf, FW, Lundquist, LL (2003) Introduction: population biology, evolution, and control of invasive species. Conserv Biol 17:24–30 CrossRefGoogle Scholar
Crawford, KM, Whitney, KD (2010) Population genetic diversity influences colonization success. Mol Ecol 19:1253–1263 Google Scholar
Cuda, JP, Ferriter, AP, Manrique, V, Medal, JC (2006) Florida’s Brazilian Peppertree Management Plan: Recommendations from the Brazilian Peppertree Task Force. West Palm Beach, FL: Florida Exotic Pest Plant Council. 82 pGoogle Scholar
Dawkins, K, Esiobu, N (2016) Emerging insights on Brazilian pepper tree (Schinus terebinthifolius) invasion: the potential role of soil microorganisms. Front Plant Sci 7, 10.3389/fpls.2016.00712Google Scholar
Ewel, JJ, Ojima, DS, Karl, DA, DeBusk, WF (1982) Schinus in Successional Ecosystems of Everglades National Park. Technical Report T-676. Homestead, FL: Everglades National Park, South Florida Research Center. 141 pGoogle Scholar
Geiger, JH, Pratt, PD, Wheeler, GS, Williams, DA (2011) Hybrid vigor for the invasive exotic Brazilian peppertree (Schinus terebinthifolius Raddi., Anacardiaceae) in Florida. Int J Plant Sci 172:655–663 Google Scholar
Grotkopp, E, Rejmanék, M (2007) High seedling relative growth rate and specific leaf area are traits of invasive species: phylogenetically independent contrasts of woody angiosperms. Am J Bot 94:525–532 Google Scholar
Iles, DT, Salguero-Gomez, R, Adler, PB, Koons, DN (2016) Linking transient dynamics and life history to biological invasion success. J Ecol 104:399–408 CrossRefGoogle Scholar
Lavergne, S, Thompson, JD, Garnier, E, Debussche, M (2004) The biology and ecology of narrow endemic and widespread plants: a comparative study of trait variation in 20 congeneric pairs. Oikos 107:505–518 Google Scholar
McDowell, SCL (2002) Photosynthetic characteristics of invasive and non-invasive species of Rubus (Rosaceae). Am J Bot 89:1431–1438 Google Scholar
Moracová, L, Pyšek, P, Jarošik, V, Pergl, J (2015) Getting the right traits: reproductive and dispersal characteristics predict the invasiveness of herbaceous plant species. PLoS ONE 10, 10.1371/journal.pone.0123634Google Scholar
Morton, J (1978) Brazilian pepper—its impact on people, animals and the environment. Econ Bot 32:353–359 CrossRefGoogle Scholar
Mukherjee, A, Williams, DA, Wheeler, GS, Cuda, JP, Pal, S, Overholt, WA (2012) Brazilian peppertree (Schinus terebintifolius) in Florida and South America: evidence of a possible niche shift driven by hybridization. Biol Invasions 14:1415–1430 CrossRefGoogle Scholar
Nickerson, K, Flory, SL (2015) Competitive and allelopathic effects of the invasive shrub Schinus terebinthifolius (Brazilian peppertree). Biol Invasions 17:555–564 Google Scholar
Obeso, JR (2002) The costs of reproduction in plants. New Phytol 155:321–348 Google Scholar
Reznick, D (1985) Cost of reproduction: an evaluation of the empirical evidence. Oikos 44:257–267 CrossRefGoogle Scholar
Smith, CC (1976) When and how much to reproduce: the trade-off between power and efficiency. Am Zool 16:763–774 CrossRefGoogle Scholar
Tho, BT, Sorrell, BK, Lambertini, C, Eller, F, Brix, H (2016) Phragmites australis: How do genotypes of different phylogeographic origins differ from their invasive genotypes in growth nitrogen allocation and gas exchange? Biol Invasions 18:2563–2576 Google Scholar
Tobe, JD, Craddock Burks, K., Cantrell, RW, Garland, MA, Sweeley, ME, Hall, DW, Wallace, P, Anglin, G, Nelson, G, Cooper, JR, Bickner, D, Gilbert, K, Aymond, N, Greenwood, K, Raymond, N (1998) Florida Wetland Plants: An Identification Manual. Tallahassee, FL: Florida Department of Environmental Protection. 588 pGoogle Scholar
Weiner, J, Campbell, LG, Pino, J, Echarte, L (2009) The allometry of reproduction within plant populations. J Ecol 97:1220–1233 Google Scholar
Williams, DA, Overholt, WA, Cuda, JP, Hughes, CR (2005) Chloroplast and microsatellite DNA diversities reveal the introduction history of Brazilian peppertree (Schinus terebinthifolius) in Florida. Mol Ecol 14:3643–3656 Google Scholar
Williams, DA, Muchugu, E, Overholt, WA, Cuda, JP (2007) Colonization patterns of the invasive Brazilian peppertree, Schinus terebinthifolius, in Florida. Heredity 98:284–293 Google Scholar