Abstract
Invasive plants cause substantial environmental damage and economic loss. Here, we explore the possibility that a selfish genetic element found in plants called cytoplasmic male sterility (CMS) could be exploited for weed control. CMS is caused by mutations in the mitochondrial genome that sterilize male reproductive organs. We developed an analytical model and a spatial simulation to assess the use of CMS alleles to manage weed populations. Specifically, we examined how fertility, selfing, pollen limitation and dispersal influenced extinction rate and time until extinction in populations where CMS arises. We found that the introduction of a CMS allele can cause rapid population extinction, but only under a restricted set of conditions. Both models suggest that the CMS strategy will be appropriate for species where pollen limitation is negligible, inbreeding depression is high and the fertility advantage of females over hermaphrodites is substantial. In general, spatial structure did not have a strong influence on the simulation outcome, although low pollen dispersal and intermediate levels of seed dispersal tended to reduce population extinction rates. Given these results, the introduction of CMS alleles into a population of invasive plants probably represents an effective control method for only a select number of species.
Highlights
The economic and environmental impact of weeds and invasive plants is profound
(3) What is the effect of spatial structure on the probability of population extinction? To address this question, we developed a spatially explicit model and ran simulations to examine the influence of pollen and seed dispersal on the fate of the cytoplasmic male sterility (CMS) allele
Genetic control represents an alternative to these conventional methods and has been applied successfully in some insect taxa, but the utility of such methods have not been assessed in plants
Summary
No global estimates are available, introduced weed species are responsible for approximately US$23.4 billion in annual crop losses in the United States (Myers and Bazely 2003) and AU$3.9 billion in Australia (Sinden et al 2004). Alien weeds are spreading through US wildlife habitat at a rate of approximately 700 000 ha/year (Babbitt 1998). These invasive weeds have a negative impact on native species directly, through out-competing and hybridizing with indigenous species (Myers and Bazely 2003; Pimentel et al 2005), and indirectly, through modifying physical features of their environment (Vitousek et al 1987; Sala et al 1996; Mack and D’Antonio 1998). In response to a 2009 The Authors Journal compilation a 2009 Blackwell Publishing Ltd 2 (2009) 555–569 this problem, numerous strategies have been employed to manage the global epidemic of invasive weeds
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