Distribution, demography and dispersal model of spatial spread of invasive plant populations with limited data

被引:28
作者
Adams, Vanessa M. [1 ,2 ]
Petty, Aaron M. [1 ,2 ]
Douglas, Michael M. [1 ,2 ]
Buckley, Yvonne M. [3 ,4 ,5 ]
Ferdinands, Keith B. [6 ]
Okazaki, Tomoko [1 ,2 ]
Ko, Dongwook W. [7 ]
Setterfield, Samantha A. [1 ,2 ]
机构
[1] Charles Darwin Univ, Res Inst Environm & Livelihoods, Darwin, NT 0909, Australia
[2] Charles Darwin Univ, Northern Australia Natl Environm Res Program Hub, Darwin, NT 0909, Australia
[3] Trinity Coll Dublin, Sch Nat Sci, Dublin 2, Ireland
[4] Trinity Coll Dublin, Trinity Ctr Biodivers Res, Dublin 2, Ireland
[5] Univ Queensland, Sch Biol Sci, ARC Ctr Excellence Environm Decis, Brisbane, Qld 4072, Australia
[6] Weed Management Branch, Dept Land Resource Management, Palmerston, NT 0831, Australia
[7] Charles Darwin Univ, Res Inst Environm & Livelihoods, Darwin, NT 0909, Australia
来源
METHODS IN ECOLOGY AND EVOLUTION | 2015年 / 6卷 / 07期
关键词
biosecurity; individual-based model; invasive plant management; invasive plants; spatially explicit spread; spread model; SPECIES DISTRIBUTION; CLIMATE-CHANGE; CONSEQUENCES; DYNAMICS; MANAGEMENT; QUANTITY; BEHAVIOR; IMPACTS; RISKS;
D O I
10.1111/2041-210X.12392
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
Invasive weeds are a major cause of biodiversity loss and economic damage world-wide. There is often a limited understanding of the biology of emerging invasive species, but delay in action may result in escalating costs of control, reduced economic returns from management actions and decreased feasibility of management. Therefore, spread models that inform and facilitate on-ground control of invasions are needed. We developed a spatially explicit, individual-based spread model that can be applied to both data-poor and data-rich situations to model future spread and inform effective management of the invasion. The model is developed using a minimum of two mapped distributions for the target species at different times, together with habitat suitability variables and basic population data. We present a novel method for internally calibrating the reproduction and dispersal distance parameters. We use a sensitivity analysis to identify variables that should be prioritized in future research to increase robustness of model predictions. We apply the model to two case studies, gamba grass and para grass, to provide management advice on emerging weed priorities in northern Australia. For both species, we find that the current extent of invasion in our study regions is expected to double in the next 10years in the absence of management actions. The predicted future distribution identifies priority areas for eradication, control and containment to reduce the predicted increase in infestation. The model was built for managers and policymakers in northern Australia working on species where expert knowledge and environmental data are often lacking, but is flexible and can be easily adapted for other situations, for example where good data are available. The model provides predicted probability of occurrence over a user-specified, typically short-term, time horizon. This output can be used to direct surveillance and management actions to areas that have the highest likelihood of rapid invasion and spread. Directing efforts to these areas provides the greatest likelihood of management success and maximizes the return on investment in management response.
引用
收藏
页码:782 / 794
页数:13
相关论文
共 52 条
[1]   Intensity analysis to unify measurements of size and stationarity of land changes by interval, category, and transition [J].
Aldwaik, Safaa Zakaria ;
Pontius, Robert Gilmore, Jr. .
LANDSCAPE AND URBAN PLANNING, 2012, 106 (01) :103-114
[2]   Dynamics of range margins for metapopulations under climate change [J].
Anderson, B. J. ;
Akcakaya, H. R. ;
Araujo, M. B. ;
Fordham, D. A. ;
Martinez-Meyer, E. ;
Thuiller, W. ;
Brook, B. W. .
PROCEEDINGS OF THE ROYAL SOCIETY B-BIOLOGICAL SCIENCES, 2009, 276 (1661) :1415-1420
[3]   Lightweight unmanned aerial vehicles will revolutionize spatial ecology [J].
Anderson, Karen ;
Gaston, Kevin J. .
FRONTIERS IN ECOLOGY AND THE ENVIRONMENT, 2013, 11 (03) :138-146
[4]   Quantitative Ecological Risk Assessment of the Magela Creek Floodplain in Kakadu National Park, Australia: Comparing Point Source Risks from the Ranger Uranium Mine to Diffuse Landscape-Scale Risks [J].
Bayliss, P. ;
van Dam, R. A. ;
Bartolo, R. E. .
HUMAN AND ECOLOGICAL RISK ASSESSMENT, 2012, 18 (01) :115-151
[5]   Causes and consequences of animal dispersal strategies: relating individual behaviour to spatial dynamics [J].
Bowler, DE ;
Benton, TG .
BIOLOGICAL REVIEWS, 2005, 80 (02) :205-225
[6]   Object-based mapping of native vegetation and para grass (Urochloa mutica) on a monsoonal wetland of Kakadu NP using a Landsat 5 TM Dry-season time series [J].
Boyden, James ;
Joyce, Karen E. ;
Boggs, Guy ;
Wurm, Penny .
JOURNAL OF SPATIAL SCIENCE, 2013, 58 (01) :53-77
[7]   Integrating bioclimate with population models to improve forecasts of species extinctions under climate change [J].
Brook, Barry W. ;
Akcakaya, H. Resit ;
Keith, David A. ;
Mace, Georgina M. ;
Pearson, Richard G. ;
Araujo, Miguel B. .
BIOLOGY LETTERS, 2009, 5 (06) :723-725
[8]   Exotic Grass Invasions: Applying a Conceptual Framework to the Dynamics of Degradation and Restoration in Australia's Tropical Savannas [J].
Brooks, Kristine J. ;
Setterfield, Samantha A. ;
Douglas, Michael M. .
RESTORATION ECOLOGY, 2010, 18 (02) :188-197
[9]  
Brooks ML, 2004, BIOSCIENCE, V54, P677, DOI 10.1641/0006-3568(2004)054[0677:EOIAPO]2.0.CO
[10]  
2