Fire management to combat disease: turning interactions between threats into conservation management

As the number and intensity of threats to biodiversity increase, there is a critical need to investigate interactions between threats and manage populations accordingly. We ask whether it is possible to reduce the effects of one threat by mitigating another. We used long-term data for the long-lived resprouter, Xanthorrhoea resinosa Pers., to parameterise an individual-based population model. This plant is currently threatened by adverse fire regimes and the pathogen Phytophthora cinnamomi. We tested a range of fire and disease scenarios over various time horizons relevant to the population dynamics of the species and the practicalities of management. While fire does not kill the disease, it does trigger plant demographic responses that may promote population persistence when disease is present. Population decline is reduced with frequent fires because they promote the greatest number of germination events, but frequent fires reduce adult stages, which is detrimental in the long term. Fire suppression is the best action for the non-seedling stages but does not promote recruitment. With disease, frequent fire produced the highest total population sizes for shorter durations, but for longer durations fire suppression gave the highest population sizes. When seedlings were excluded, fire suppression was the best action. We conclude that fire management can play an important role in mitigating threats posed by this disease. The best approach to reducing declines may be to manage populations across a spatial mosaic in which the sequence of frequent fires and suppression are staggered across patches depending on the level of disease at the site.

[1]  D. Richardson,et al.  Non-linearities, synergisms and plant extinctions in South African fynbos and Australian kwongan , 1996, Biodiversity & Conservation.

[2]  M. Soulé,et al.  Mesopredator release and avifaunal extinctions in a fragmented system , 1999, Nature.

[3]  B. Dell,et al.  The long-term ability of phosphite to control Phytophthora cinnamomi in two native plant communities of Western Australia , 2001 .

[4]  M. McCarthy,et al.  Species conservation and management : case studies , 2004 .

[5]  David M. Richardson,et al.  Managing fynbos for biodiversity: constraints and options in a fire-prone environment. , 1994 .

[6]  R. Ostfeld,et al.  Climate Warming and Disease Risks for Terrestrial and Marine Biota , 2002, Science.

[7]  P. Vitousek,et al.  Biological invasions by exotic grasses, the grass/fire cycle, and global change , 1992 .

[8]  T. Wardlaw,et al.  Susceptibility of Selected Tasmanian Rare Plants to Phytophthora cinnamomi , 1995 .

[9]  Dawn M. Lawson,et al.  Habitat fragmentation and altered fire regime create trade-offs for an obligate seeding shrub. , 2010, Ecology.

[10]  B. Lamont,et al.  Seed Bank and Population Dynamics of Banksia cuneata: The Role of Time, Fire, and Moisture , 1991, Botanical Gazette.

[11]  Helen M. Regan,et al.  The persistence niche: what makes it and what breaks it for two fire-prone plant species , 2007 .

[12]  G. Weste The dieback cycle in Victorian forests: a 30-year study of changes caused by Phytophthora cinnamomi in Victorian open forests, woodlands and heathlands , 2003, Australasian Plant Pathology.

[13]  Byron B. Lamont,et al.  Turner Review No. 8. Ecology and ecophysiology of grasstrees , 2004 .

[14]  A. Gill,et al.  Flammable Australia: The Fire Regimes and Biodiversity of a Continent , 2009 .

[15]  R. Bradstock A biogeographic model of fire regimes in Australia: current and future implications , 2010 .

[16]  John L. Harper,et al.  Population Biology of Plants. , 1978 .

[17]  C. Crane,et al.  Phytophthora cinnamomi invasion, a major threatening process to conservation of flora diversity in the South-west Botanical Province of Western Australia , 2007 .

[18]  B. Wilson,et al.  Development of disease caused by Phytophthora cinnamomi in mature Xanthorrhoea australis , 2001 .

[19]  Jessica Gurevitch,et al.  Design and Analysis of Ecological Experiments , 1993 .

[20]  R. Whelan,et al.  Phytophthora Root Rot: Assessing the potential threat to Australia's oldest national park , 2006 .

[21]  Helen M. Regan,et al.  The effects of fire and predators on the long-term persistence of an endangered shrub, Grevillea caleyi , 2003 .

[22]  J. McGuire,et al.  Efficacy of two new systemic fungicides and ethazole for control of Phytophthora root rot of rhododendron, and spread of Phytophthora cinnamomi in propagation benches. , 1980 .

[23]  David W. Inouye,et al.  ENDANGERED MUTUALISMS: The Conservation of Plant-Pollinator Interactions , 1998 .

[24]  Alexandra D. Syphard,et al.  Predicting spatial patterns of fire on a southern California landscape , 2008 .

[25]  S. Pimm Lessons from a kill , 1996, Biodiversity & Conservation.

[26]  K. Lafferty,et al.  Evidence for the Role of Infectious Disease in Species Extinction and Endangerment , 2006, Conservation biology : the journal of the Society for Conservation Biology.

[27]  Gretna Weste,et al.  THE BIOLOGY OF PHYTOPHTHORA CINNAMOMI IN AUSTRALASIAN FORESTS , 1987 .

[28]  A. Andersen,et al.  Patch Mosaic Burning for Biodiversity Conservation: a Critique of the Pyrodiversity Paradigm , 2006, Conservation biology : the journal of the Society for Conservation Biology.

[29]  Keith Johnson,et al.  Quasiextinction Probabilities as a Measure of Impact on Population Growth , 1982 .

[30]  C. Margules,et al.  A SYNERGISTIC EFFECT PUTS RARE, SPECIALIZED SPECIES AT GREATER RISK OF EXTINCTION , 2004 .

[31]  G. Fox Failure Time Analysis: Studying Times-to-Events and Rates at Which Events Occur , 2001 .

[32]  B. Grant,et al.  THE COMPLEX ACTION OF PHOSPHONATES AS ANTIFUNGAL AGENTS , 1991 .

[33]  Keeley,et al.  Reexamining fire suppression impacts on brushland fire regimes , 1999, Science.

[34]  D. Maitre Effects of season of burn on the regeneration of two Proteaceae with soil-stored seed , 1988 .

[35]  B. J. Fox,et al.  FLOWERING OF XANTHORRHOEA FULVA : THE EFFECT OF FIRE AND CLIPPING , 1998 .

[36]  G. Weste Phytophthora cinnamomi - the Cause of Severe Disease in certain Native Communities in Victoria , 1974 .

[37]  N. Curtis A Post-fire Ecological Study of Xanthorrhoea australis Following Prescribed Burning in the Warby Range State Park, North-eastern Victoria, Australia , 1998 .

[38]  J. Mee The synergistic effect , 1965 .

[39]  B. Lamont,et al.  Plant size and season of burn affect flowering and fruiting of the grasstree Xanthorrhoea preissii. , 2000 .

[40]  C. Peres Synergistic Effects of Subsistence Hunting and Habitat Fragmentation on Amazonian Forest Vertebrates , 2001 .

[41]  Colin J. Thompson,et al.  Expected minimum population size as a measure of threat , 2001 .

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

[43]  C. Crane,et al.  Phosphite reduces disease extension of a Phytophthora cinnamomi front in Banksia woodland, even after fire , 2004, Australasian Plant Pathology.

[44]  C. Rosenzweig,et al.  Attributing physical and biological impacts to anthropogenic climate change , 2008, Nature.

[45]  P. Attiwill,et al.  Does manganese play a role in the distribution of the eucalypts , 2001 .

[46]  R. Bradstock,et al.  Simulation of the Effect of Spatial and Temporal Variation in Fire Regimes on the Population Viability of a Banksia Species , 1996 .

[47]  E. Menges Integrating demography and fire management: an example from Florida scrub , 2007 .

[48]  J. R. Hardison Fire and Flame for Plant Disease Control , 1976 .