Hostname: page-component-586b7cd67f-t8hqh Total loading time: 0 Render date: 2024-11-24T05:58:45.608Z Has data issue: false hasContentIssue false

Nutrient Addition and Moisture Promote the Invasiveness of Crimson Fountaingrass (Pennisetum setaceum)

Published online by Cambridge University Press:  20 January 2017

Sebataolo J. Rahlao*
Affiliation:
Centre for Invasion Biology, Department of Conservation Ecology and Entomology, Stellenbosch University, Private Bag X1, Matieland 7602, South Africa
Karen J. Esler
Affiliation:
Centre for Invasion Biology, Department of Conservation Ecology and Entomology, Stellenbosch University, Private Bag X1, Matieland 7602, South Africa
Sue J. Milton
Affiliation:
Centre for Invasion Biology, Department of Conservation Ecology and Entomology, Stellenbosch University, Private Bag X1, Matieland 7602, South Africa DST Centre of Excellence, Percy FitzPatrick Institute of African Ornithology, University of Cape Town, Rondebosch 7701, South Africa
Phoebe Barnard
Affiliation:
Climate Change and BioAdaptation Division, Kirstenbosch Research Centre, South African National Biodiversity Institute, Private Bag X7, Claremont 7735, South Africa DST Centre of Excellence, Percy FitzPatrick Institute of African Ornithology, University of Cape Town, Rondebosch 7701, South Africa
*
Corresponding author's E-mail: [email protected]

Abstract

We conducted a greenhouse study to examine the effects of different habitat conditions and environmental resources on the growth rates of crimson fountaingrass, an invasive, alien, perennial grass in South Africa. To help understand the factors promoting the spread of this emergent alien grass, we investigated the effects of temperature regimes, nutrient and moisture addition, and soil type on seedling growth rates and biomass allocation. Our results suggest that crimson fountaingrass seedlings do not tolerate drought because they died within 1 mo without water. Additional nutrients and extra water increased seedling growth rates throughout the study period. Higher temperatures with extra moisture increased seedling growth rates and the development of belowground biomass throughout the study period. This study demonstrates the importance of available environmental resources and their interaction with some habitat conditions in promoting crimson fountaingrass growth. We suggest that soil moisture and nutrient availability are critical factors affecting successful establishment of crimson fountaingrass in arid environments. Managers should target seedlings for removal following precipitation and in areas of nutrient enrichment, such as near rivers and at road–river crossings.

Type
Research Article
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

Alvarez-Aquino, , Williams-Linera, C. G., and Newton, A. C. 2004. Experimental native tree seedling establishment for the restoration of a Mexican cloud forest. Restor. Ecol. 12:412418.CrossRefGoogle Scholar
Brooks, M. L. and Pyke, D. A. 2001. Invasive plants and fire in the deserts of North America. Pages 114. In Galley, K. E. M. and Wilson, T. P. Proceedings of the Invasive Species Workshop: the Role of Fire in the Control and Spread of Invasive Species. Fire conference 2000: The First National Congress on Fire Ecology, Prevention, and Management. Tallahassee, FL Tall Timbers Research Station Miscellaneous Publication 11.Google Scholar
Daehler, C. C. 2003. Performance comparisons of co-occurring native and alien invasive plants: implications for conservation and restoration. Annu. Rev. Ecol. Syst. 34:183211.CrossRefGoogle Scholar
Daehler, C. C. and Goergen, E. M. 2005. Experimental restoration of an indigenous Hawaiian grassland after invasion by buffel grass (Cenchrus ciliaris). Restor. Ecol. 13:380389.CrossRefGoogle Scholar
Davis, M. A., Grime, P. J., and Thompson, K. 2000. Fluctuating resources in plant communities: a general theory of invasibility. J. Ecol. 88:528534.CrossRefGoogle Scholar
Dukes, J. S. and Mooney, H. A. 1999. Does global change increase the success of biological invaders? Trends Ecol. Evol. 14:135139.CrossRefGoogle ScholarPubMed
Goergen, E. and Daehler, C. C. 2002. Factors affecting seedling recruitment in an invasive grass (Pennisetum setaceum) and a native grass (Heteropogon contortus) in the Hawaiian Islands. Plant Ecol. 161:141156.CrossRefGoogle Scholar
Joubert, D. and Cunningham, P. L. 2002. The distribution and invasive potential of fountain grass Pennisetum setaceum in Namibia. Dinteria. 27:3747.Google Scholar
Milton, S. J., Hoffmann, J. H., Bowie, R. C. K., D'Amico, J., Griffiths, M., Joubert, D., Loewenthal, D., Moinde, N. N., Seymour, C., Toral-Granda, M. V., and Wiseman, R. 1998. Invasive fountain grass on the Cape Peninsula. S. Afr. J. Sci. 94:5759.Google Scholar
Noy-Meir, I. 1973. Desert ecosystems: environment and producers. Annu. Rev. Ecol. Syst. 4:2551.CrossRefGoogle Scholar
Poulin, J., Sakai, A. K., Weller, S. G., and Nguyen, T. 2007. Phenotypic plasticity, precipitation, and invasiveness in the fire-promoting grass Pennisetum setaceum (Poaceae). Am. J. Bot. 94:533541.CrossRefGoogle ScholarPubMed
Rahlao, S. J. 2009. Current and Future Vulnerability of South African Ecosystems to Perennial Grass Invasions under Global Change Scenarios. . Stellenbosch, South Africa Stellenbosch University.Google Scholar
Rahlao, S. J., Milton, S. J., Esler, K. J., van Wilgen, B. W., and Barnard, P. 2009. Effects of invasion of fire-free arid shrublands by a fire-promoting invasive alien grass Pennisetum setaceum in South Africa. Austral Ecol. 34:920928.CrossRefGoogle Scholar
Rejmánek, M., Richardson, D. M., and Pysek, P. 2004. Plant invasions and invasibility of plant communities. Pages 332355. In van der Maarel, E. Vegetation Ecology. Oxford, UK Blackwell.Google Scholar
Reynolds, J. F., Kemp, P. R., Ogle, K., and Fernández, R. J. 2004. Modifying the ‘pulse–reserve’ paradigm for deserts of North America: precipitation pulses, soil water, and plant responses. Oecologia. 141:194210.CrossRefGoogle ScholarPubMed
Richards, C. L., Bossdorf, O., Muth, N. Z., Gurevitch, J., and Pigliucci, M. 2006. Jack of all trades, master of some? on the role of phenotypic plasticity in plant invasions. Ecol. Lett. 9:981993.CrossRefGoogle ScholarPubMed
Tunison, J. T. 1992. Fountain grass control in Hawaii Volcanoes National Park: management considerations and strategies. Pages 376393. In Stone, C. P., Smith, C. W., and Tunison, J. T. Alien Plant Invasions in Native Ecosystems of Hawaii. Honolulu, HI University of Hawaii Press.Google Scholar
Ward, J. P., Smith, S. E., and McClaran, M. P. 2006. Water requirements for emergence of buffelgrass (Pennisetum ciliare). Weed Sci. 54:720725.CrossRefGoogle Scholar
Williams, D. G. and Black, R. A. 1993. Phenotypic variation in contrasting temperature environments: growth and photosynthesis in Pennisetum setaceum from different altitudes on Hawaii. Funct. Ecol. 7:623633.CrossRefGoogle Scholar
Williams, D. G. and Black, R. A. 1994. Drought response of a native and introduced Hawaiian grass. Oecologia. 97:512519.CrossRefGoogle ScholarPubMed
Williams, D. G., Mack, R. N., and Black, R. A. 1995. Ecophysiology of introduced Pennisetum setaceum on Hawaii: the role of phenotypic plasticity. Ecology. 76:15691580.CrossRefGoogle Scholar
Wilson, A. M., Harris, G. A., and Gates, D. H. 1966. Fertilization of mixed cheatgrass–blue bunch wheatgrass stands. J. Range Manag. 19:134137.CrossRefGoogle Scholar