Fire persistence traits of plants along a productivity and disturbance gradient in mediterranean shrublands of south‐east Australia

Aim To understand changes in fire persistence traits of plants along a latitudinal gradient, considering the interactions between productivity, community (fuel) structure and fire regime. Location A gradient in the south of Australia (latitude 33‐37 ° S; longitude 140‐ 143 ° E), including: Little Desert National Park (VIC), Big Desert Wilderness Park (VIC), Murray-Sunset National Park (VIC), Danggali Conservation Park (SA) and Ta rawi Nature Reserve (NSW). Methods We selected four areas along a latitudinal gradient for which information on fire history and vegetation was available. Then, we tested to what extent the four selected areas have different climate and different fire regimes. Plant cover values of different life forms provided an indication of the plant community structure and flammability, and the proportion of species with different fire persistence traits (resprouting, seedbank persistence) informed us on the trait selection. Results Precipitation decreases and temperature increases from south to north. Thus the selected sites represent a gradient from high productivity (low aridity) in the south to low productivity (high aridity) in the north. Fire statistics suggest that fire frequency parallels productivity. There is a tendency for life form dominance and community structure to shift in such a way that fuel connectivity is reduced towards the north. Resprouting species increase and obligate seeders decrease along the fire‐productivity gradient. Main conclusions Changes in plant traits are difficult to understand without simultaneous consideration of both the disturbance and the productivity gradients. In our study area, fire regime and productivity interact in such a way that decreases in productivity imply changes in fuel structure that produce a reduction in fire frequency. Resprouting species are better represented at the high fire‐productivity part of the gradient, while obligate seeders are better represented at the opposite end of the gradient. The results also emphasize the importance of considering not only climate changes but also changes in fuel structure to predict future fire regimes.

[1]  Juli G. Pausas,et al.  Inferring differential evolutionary processes of plant persistence traits in Northern Hemisphere Mediterranean fire‐prone ecosystems , 2006 .

[2]  P. Clarke,et al.  Landscape patterns of woody plant response to crown fire: disturbance and productivity influence sprouting ability , 2005 .

[3]  Juli G. Pausas,et al.  Plant persistence traits in fire-prone ecosystems of the Mediterranean basin: a phylogenetic approach , 2005 .

[4]  J. Miller,et al.  The vegetation of the Scotia 1: 100 000 map sheet, western New South Wales , 2005 .

[5]  M. Westoby,et al.  Sprouting by semi‐arid plants: testing a dichotomy and predictive traits , 2004 .

[6]  Philip Gibbons,et al.  Australian Plant Communities. Dynamics of Structure, Growth and Biodiversity , 2004 .

[7]  Jon E. Keeley,et al.  PLANT FUNCTIONAL TRAITS IN RELATION TO FIRE IN CROWN-FIRE ECOSYSTEMS , 2004 .

[8]  M. Westoby,et al.  Sprouting ability across diverse disturbances and vegetation types worldwide , 2004 .

[9]  R. Bradstock,et al.  Fire-mediated effects of overstorey on plant species diversity and abundance in an eastern Australian heath , 2003, Plant Ecology.

[10]  Ross K. Meentemeyer,et al.  Landscape-scale patterns of shrub-species abundance in California chaparral – The role of topographically mediated resource gradients , 2001, Plant Ecology.

[11]  I. Noble,et al.  The use of vital attributes to predict successional changes in plant communities subject to recurrent disturbances , 1980, Vegetatio.

[12]  Takuya Kubo,et al.  Optimal size of storage for recovery after unpredictable disturbances , 2004, Evolutionary Ecology.

[13]  P. J. Myerscough Flammable Australia. The Fire Regimes and Biodiversity of a Continent , 2003 .

[14]  L. Hughes Climate change and Australia: Trends, projections and impacts , 2003 .

[15]  R. Bradstock,et al.  An application of plant functional types to fire management in a conservation reserve in southeastern Australia , 2003 .

[16]  D. Ackerly Community Assembly, Niche Conservatism, and Adaptive Evolution in Changing Environments , 2003, International Journal of Plant Sciences.

[17]  Damian Barrett,et al.  Estimating regional terrestrial carbon fluxes for the Australian continent using a multiple‐constraint approach , 2003 .

[18]  F. Woodward,et al.  What controls South African vegetation — climate or fire? , 2003 .

[19]  Damian J. Barrett,et al.  Estimating regional terrestrial carbon fluxes for the Australian continent using a multiple-constraint approach I. Using remotely sensed data and ecological observations of net primary production , 2003 .

[20]  P. Clarke,et al.  Post-fire response of shrubs in the tablelands of eastern Australia: do existing models explain habitat differences? , 2002 .

[21]  R. A. Bradstock,et al.  Fire regimes and biodiversity in semi-arid mallee ecosystems. , 2002 .

[22]  J. Pausas Resprouting vs seeding – a Mediterranean perspective , 2001 .

[23]  Nigel J. Tapper,et al.  The Sensitivity of Australian Fire Danger to Climate Change , 2001 .

[24]  W. Bond,et al.  Dynamics of the overstorey and species richness in Australian heathlands , 2001 .

[25]  W. Bond,et al.  Ecology of sprouting in woody plants: the persistence niche. , 2001, Trends in ecology & evolution.

[26]  C. Loehle Strategy Space and the Disturbance Spectrum: A Life‐History Model for Tree Species Coexistence , 2000, The American Naturalist.

[27]  Peter J. Bellingham,et al.  Resprouting as a life history strategy in woody plant communities , 2000 .

[28]  M. Verdú Ecological and evolutionary differences between Mediterranean seeders and resprouters , 2000 .

[29]  Juli G. Pausas,et al.  Response of plant functional types to changes in the fire regime in Mediterranean ecosystems: A simulation approach , 1999 .

[30]  Juli G. Pausas,et al.  Post-fire regeneration patterns in the eastern Iberian Peninsula , 1999 .

[31]  A. Hahs,et al.  Plant communities, species richness and their environmental correlates in the sandy heaths of Little Desert National Park, Victoria , 1999 .

[32]  Neal J. Enright,et al.  The ecological significance of canopy seed storage in fire‐prone environments: a model for resprouting shrubs , 1998 .

[33]  F. Ojeda Biogeography of seeder and resprouter Erica species in the Cape Floristic Region—Where are the resprouters? , 1998 .

[34]  J. Keeley Coupling Demography, Physiology and Evolution in Chaparral Shrubs , 1998 .

[35]  Andrew Benwell Post-fire Seedling Recruitment in Coastal Heathland in Relation to Regeneration Strategy and Habitat , 1998 .

[36]  Tom Beer,et al.  Estimating australian forest fire danger under conditions of doubled carbon dioxide concentrations , 1995 .

[37]  A. Markey,et al.  Biogeography of Fire-Killed and Resprouting Banksia Species in South-Western Australia , 1995 .

[38]  T. Auld Soil seedbank patterns of four trees and shrubs from arid Australia , 1995 .

[39]  M. Westoby,et al.  Herbivorous arthropods on bracken (Pteridium aquilinum (L.) Khun) in Australia compared with elsewhere , 1992 .

[40]  M. Westoby,et al.  Germination biology of selected central Australian plants , 1992 .

[41]  C. Herrera,et al.  Historical Effects and Sorting Processes as Explanations for Contemporary Ecological Patterns: Character Syndromes in Mediterranean Woody Plants , 1992, The American Naturalist.

[42]  D. Richardson,et al.  Coexistence of Seeders and Sprouters in a Fire-Prone Environment: the Role of Ecophysiology and Soil Moisture , 1992 .

[43]  R. A. Bradstock,et al.  Mediterranean Landscapes in Australia: Mallee Ecosystems and Their Management , 1989 .

[44]  J. Noble Fire studies in mallee (Eucalyptus spp.) communities of western New South Wales: The effects of fires applied in different seasons on herbage productivity and their implications for management , 1989 .

[45]  D. Hilbert A model of life history strategies of chaparral shrubs in relation to fire frequency , 1987 .

[46]  Jon E. Keeley,et al.  Resilience of mediterranean shrub communities to fires , 1986 .

[47]  C. E. Van Wagner,et al.  The theory and use of two fire history models , 1985 .

[48]  R. Bigalke,et al.  Fire in Fynbos , 1984 .

[49]  N. M. Tainton,et al.  Ecological Effects of Fire in South African Ecosystems , 1984, Ecological Studies.

[50]  J. Keeley,et al.  Reproduction of Chaparral Shrubs After Fire: A Comparison of Sprouting and Seeding Strategies , 1978 .

[51]  M. Rosenzweig Net Primary Productivity of Terrestrial Communities: Prediction from Climatological Data , 1968, The American Naturalist.