The importance of flood events on the establishment of seedlings and cuttings of saltcedar (Tamarix ramosissima)

Authors

  • Evangelina Natale Universidad Nacional de Río Cuarto - Dpto de Ciencias Naturales
  • Herminda Reinoso Universidad Nacional de Río Cuarto - Dpto de Ciencias Naturales

DOI:

https://doi.org/10.25260/EA.16.26.2.0.87

Abstract

The expansion of invasive plants is considered one of the greatest threats to biodiversity. The environments more threatened by the presence of exotic invasive species are the riparian areas due to their small surface and high diversity. The advance of Tamarix in these environments may be linked to transient conditions of higher water availability, which would allow initial colonization. The objective of the present work was to determine which hydric conditions promote germination and establishment of Tamarix cuttings by measuring in the laboratory the effects of different periods of flooding. It was observed that the germination was high under irrigation at field capacity and was decreased after 10 days of flood, while the establishment through cuttings required at least 15 days duration of a flood event. These results will contribute to the identification of critical environmental conditions that facilitate the establishment of the genus in new areas and guide actions for its early control.

Author Biographies

Evangelina Natale, Universidad Nacional de Río Cuarto - Dpto de Ciencias Naturales

Ayudante de primera dedicación semi-exclusiva

Herminda Reinoso, Universidad Nacional de Río Cuarto - Dpto de Ciencias Naturales

Profesor asociado dedicacíon exclusiva

References

Baker, HG. 1974. The evolution of weeds. Annual Review of Ecology and Systematics, 9:1-24.

Davis, MA; JP Grime & K Thompson. 2000. Fluctuating resources in plant communities: a general theory of invisibility. Journal of Ecology, 88:258-534.

De Loach, CJ; RI Carruthers; JE Lovich; TL Dudley & SD Smith. 2000. Ecological interactions in the biological control of salt cedar (Tamarix spp.) in the United States: towards a new understanding. Pp. 819-873 in: Spencer, NR (ed.). Proceedings of the X International Symposium on Biological Control of Weeds. Montana State University, Bozeman, Montana.

Di Tomaso, JM. 1998. Impact, biology, and ecology of saltcedar (Tamarix spp.) in the Southwestern United States. Weed Technology, 12:326-336.

Drew, M. 1997. Oxygen deficiency and metabolism: injury and acclimation under hypoxia and anoxia. Annual Review of Plant Physiology and Plant Molecular Biology, 48:223-250.

Gilbert, G & MJ Lechovicz. 2005. Invasibility and abiotic gradients: the positive correlation between native and exotic plant diversity. Ecology, 86:1848-1855.

Glenn, EP & PM Nagler. 2005. Comparative ecophysiology of Tamarix ramosissima and native trees in western U.S. riparian zones. Journal of Arid Environments, 61:419-446.

Glenn, E; R Tanner; S Mendez; T Kehret; D Moorem; et al. 1998. Growth rates, salt tolerance and water use characteristics of native and invasive riparian plants from the delta of the Colorado River, Mexico. Journal of Arid Environments, 40:281-294.

Hartmann, T & D Kester. 1988. Propagación de plantas: principios y prácticas. Compañía Editorial Continental. México, D.F.

Kulichikhin, KY; TV Chirkova & K Fagerstedt. 2008. Intracellular pH in rice and wheat root tips under hypoxic and anoxic conditions. Plant Signal. Behav., 3:240-242.

Matthews, S. 2005. GISP El Programa Mundial Sobre Especies Invasoras. 1a edición. ISBN 1-919684-49-2.

Natale, E; AJ Oggero; D Marini & H Reinoso. 2014. Restauración de bosque nativo en un área invadida por Tamariscos (Tamarix ramossisima) en el sur de la provincia de Córdoba, Argentina. Ecosistemas, 23:130-136.

Natale, E; SM Zalba; H Reinoso & G Damilano. 2012. Assessing invasion process through pathway and vector analysis: case of Saltcedar (Tamarix spp.). Management of Biological Invasion, 3:37-44.

Natale, E; SM Zalba; A Oggero & H Reinoso. 2010. Establishment of Tamarix ramosissima under different conditions of salinity and water availability: Implications for its management as an invasive species. Journal of Arid Environment, 74:1399-1407.

Natale, E; J Gaskin; SM Zalba; M Ceballos & H Reinoso. 2008. Especies del género Tamarix (Tamaricaceae) invadiendo ambientes naturales y seminaturales de Argentina. Boletín de la Sociedad Argentina de Botánica, 43:135-145.

Pardos, JA. 2004. Respuestas de las plantas al anegamiento del suelo. Investigaciones Agrarias: Sistema de Recursos Forestales. Fuera de Serie. Pp. 101-107.

Reynolds, LV; DJ Cooper & NT Hobbs. 2014. Drivers of riparian tree invasión on a desert stream. River Resource Application, 30:60-70.

Shafroth, PB; JR Clever; L Dudley; J Stuart; JP Taylor; et al. 2005. Control of Tamarix in the western U.S. -implications for water salvage, wildlife use, and riparian restoration. Environmental Management, 35:231-246.

Zalba, SM; A Cuevas & R. Boó. 2008. Aleppo pine invasion after a wildfire in an Argentinean grassland nature reserve. Journal of Environmental Management, 88:539-546.

Importancia de eventos de inundación sobre el establecimiento de plántulas y estacas de tamariscos (Tamarix ramosissima)

Downloads

Published

2016-02-10

How to Cite

Natale, E., & Reinoso, H. (2016). The importance of flood events on the establishment of seedlings and cuttings of saltcedar (Tamarix ramosissima). Ecología Austral, 26(1), 1–6. https://doi.org/10.25260/EA.16.26.2.0.87