ECOHYDROLOGY Ecohydrol. (2016) Published online in Wiley Online Library (wileyonlinelibrary.com) DOI: 10.1002/eco.1742 Potential of grass invasions in desert shrublands to create novel ecosystem states under variable climate Kailiang Yu, 1 * Gregory S. Okin, 2 Sujith Ravi 3 and Paolo D’Odorico 1,4 Department of Environmental Sciences, University of Virginia, Charlottesville, VI, USA Department of Geography, University of California, Los Angeles, CA, USA Department of Earth and Environmental Sciences, Temple University, Philadelphia, PA, USA National Socio-Environmental Synthesis Center, University of Maryland, Annapolis, MD, USA ABSTRACT The invasion of exotic grasses into shrublands is a major disturbance to dryland ecosystems. The presence of exotic grasses enhances the occurrence of wildfire in landscapes that had not evolved in the presence of fire, leading to high rates of mortality of the native vegetation. Exotic grasses could be more prone to water stress and mortality than the shrubs they replaced and may not establish during drought, facts that are crucial in ecosystems undergoing increased climatic variability. Here, we develop a process-based modelling framework to investigate the complex dynamics resulting from the introduction of exotic grasses under variable climate. We find that the system converges towards different steady states, depending on the magnitude of climatic variability. While in the absence of climate fluctuations the shrubland state is replaced by an exotic grassland, interannual climate variability may inhibit grass invasion and stabilize the shrubland state. However, climatic variability also gives rise to a novel third, unvegetated state, with grass invasion being followed by drought, grass mortality and intense soil erosion. Most of the research on climate change effects on ecosystems has historically concentrated on the ecological impact of shifts in mean climate conditions. This study shows that changes in the variance are also important when shifts in vegetation composition (e.g. species invasions) result in different susceptibility to climatic variability. In the presence of random climate fluctuations, ecosystems can display steady states that differ from those that would exist under a constant climate or with a climate trend. Copyright © 2016 John Wiley & Sons, Ltd. Supporting information may be found in the online version of this article. KEY WORDS invasive species; fire cycle; climate variability; exotic grasses; unvegetated state Received 15 October 2015; Revised 18 March 2016; Accepted 28 March 2016 INTRODUCTION Biological invasions are recognized as major contributors to global environmental change (Vitousek et al., 1997; Mooney and Cleland, 2001). It has been observed that biological invasions affect ecosystem dynamics not only through their direct impact on resource competition and pool of available species (e.g. Olsson et al., 2012) but also indirectly through their ability to modify the disturbance regime. For example, invasive plants may change fire intensity and frequency or alter the rate of abiotic processes such as soil erosion (D’Antonio and Vitousek, 1992; Ziska et al., 2005; Miller et al., 2010). This disturbance-mediated effect of species invasions on ecosystems is observed when the invader is functionally different from the native species, *Correspondence to: Kailiang Yu, Department of Environmental Sciences, University of Virginia, Charlottesville, VI, USA. E-mail: ky9hc@virginia.edu Copyright © 2016 John Wiley & Sons, Ltd. i.e. when it exhibits some traits that (i) affect the disturbance regime and (ii) are missing in the native population (D’Antonio, 2000). For example, the invasion of desert shrublands by exotic annual and perennial grasses has been observed to lead to an increase in fire frequency and intensity because of the increase in grass fuel and in connectivity of vegetation cover (Okin et al., 2009a). The introduction of fires in shrubland ecosystems, where burning has not been historically a major selective force, results in an increase in the mortality rates of shrubland species, particularly if they are not adapted to fire (e.g. Bond et al., 2005; Runyan et al., 2012). The loss of shrub biomass further enhances the establishment and spread of invasive grasses (D’Antonio, 2000). Known as ‘the fire cycle’ (D’Antonio and Vitousek, 1992), this positive feedback leads to the replacement of fire-intolerant native shrubs with exotic grasses (Figure 1). The grass-fire feedback may induce stable grass-dominated vegetated states in arid and semiarid environments (Grigulis et al., 2005; Keeley and Rundel, 2005), even when shrubs have