Proceedings of the Third International Conference on Invasive ...
Proceedings of the Third International Conference on Invasive ...
Proceedings of the Third International Conference on Invasive ...
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<str<strong>on</strong>g>Proceedings</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>Third</str<strong>on</strong>g> <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong> <strong>Invasive</strong> SpartinaChapter 2: Spartina Distributi<strong>on</strong> and SpreadMODELING THE SPREAD OF INVASIVE SPARTINA HYBRIDS IN SAN FRANCISCO BAYR.J. HALL,A.M.HASTINGS AND D.R. AYRESUniversity <str<strong>on</strong>g>of</str<strong>on</strong>g> California, Davis, One Shields Ave., Davis, CA 95616; rjhall@ucdavis.eduThe emergence <str<strong>on</strong>g>of</str<strong>on</strong>g> highly fit hybrids between native and introduced species is an increasinglywidespread problem that can impact entire ecosystems. In San Francisco Bay, a swarm <str<strong>on</strong>g>of</str<strong>on</strong>g> hybridcordgrass (Spartina foliosa x alterniflora) is covering vast areas <str<strong>on</strong>g>of</str<strong>on</strong>g> intertidal mudflat, threatening <str<strong>on</strong>g>the</str<strong>on</strong>g>native S. foliosa with extincti<strong>on</strong>. Here we outline a modeling approach for assessing <str<strong>on</strong>g>the</str<strong>on</strong>g> relativeimportance <str<strong>on</strong>g>of</str<strong>on</strong>g> elevated hybrid fitness traits in explaining <str<strong>on</strong>g>the</str<strong>on</strong>g> rapidity <str<strong>on</strong>g>of</str<strong>on</strong>g> this invasi<strong>on</strong>. Wedem<strong>on</strong>strate that elevated growth rate, seedling survival and pollen producti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> hybrids relative to<str<strong>on</strong>g>the</str<strong>on</strong>g> native species interact to predict <str<strong>on</strong>g>the</str<strong>on</strong>g> observed faster-than-exp<strong>on</strong>ential spread <str<strong>on</strong>g>of</str<strong>on</strong>g> cordgrassthrough <str<strong>on</strong>g>the</str<strong>on</strong>g> Bay.Keywords: invasi<strong>on</strong>, model, hybridizati<strong>on</strong>, SpartinaINTRODUCTIONAn exotic introduced into a new range is <str<strong>on</strong>g>of</str<strong>on</strong>g>tenphenomenally successful; this may be due to exploitati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g>a previously unfilled niche, a release from natural enemies,or increased competitive ability relative to <str<strong>on</strong>g>the</str<strong>on</strong>g> native biota(Williams<strong>on</strong> 1996). However, in many ecosystems, <str<strong>on</strong>g>the</str<strong>on</strong>g>emergence <str<strong>on</strong>g>of</str<strong>on</strong>g> hybrids between native and exotic species is<str<strong>on</strong>g>the</str<strong>on</strong>g> greatest threat to local biodiversity, particularly if <str<strong>on</strong>g>the</str<strong>on</strong>g>hybrids have superior fecundity or suvivorship comparedwith <str<strong>on</strong>g>the</str<strong>on</strong>g> native (Wolf et al. 2001). An example <str<strong>on</strong>g>of</str<strong>on</strong>g> this is <str<strong>on</strong>g>the</str<strong>on</strong>g>invasi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> hybrid cordgrass Spartina foliosa x alterniflorain San Francisco Bay. Since <str<strong>on</strong>g>the</str<strong>on</strong>g> introducti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> S.alterniflora in <str<strong>on</strong>g>the</str<strong>on</strong>g> 1970s, hybrids have emerged whosegrowth rates, fecundity and tolerance to envir<strong>on</strong>mentalc<strong>on</strong>diti<strong>on</strong>s exceed that <str<strong>on</strong>g>of</str<strong>on</strong>g> both parental lineages (Ayres et al.2003). The hybrids impact <strong>on</strong> many organisms in <str<strong>on</strong>g>the</str<strong>on</strong>g> Bayby covering open mudflat crucial to feeding shorebirds,and changing <str<strong>on</strong>g>the</str<strong>on</strong>g> tidal pr<str<strong>on</strong>g>of</str<strong>on</strong>g>ile through sedimentaccumulated in <str<strong>on</strong>g>the</str<strong>on</strong>g>ir root mass. C<strong>on</strong>trary to classicalecological <str<strong>on</strong>g>the</str<strong>on</strong>g>ory, which suggests that a species withunlimited resources can grow at most exp<strong>on</strong>entially (e.g.,Turchin 2003), <str<strong>on</strong>g>the</str<strong>on</strong>g> area covered by hybrid cordgrass in <str<strong>on</strong>g>the</str<strong>on</strong>g>Bay has increased super-exp<strong>on</strong>entially (i.e. <str<strong>on</strong>g>the</str<strong>on</strong>g> growth rateper unit area is increasing through time; Fig. 1). If thisinvasi<strong>on</strong> c<strong>on</strong>tinues unchecked, it seems likely that <str<strong>on</strong>g>the</str<strong>on</strong>g>native S. foliosa is doomed to extincti<strong>on</strong> throughintrogressi<strong>on</strong> (Ayres et al. 2003).In order to design effective c<strong>on</strong>trol strategies, it is vitalto determine <str<strong>on</strong>g>the</str<strong>on</strong>g> key hybrid traits resp<strong>on</strong>sible for drivingthis invasi<strong>on</strong>. Increased vegetative growth rates, elevatedpollen producti<strong>on</strong> and seedling survival <str<strong>on</strong>g>of</str<strong>on</strong>g> hybrid Spartinarelative to <str<strong>on</strong>g>the</str<strong>on</strong>g> native have all been proposed as c<strong>on</strong>tributingto <str<strong>on</strong>g>the</str<strong>on</strong>g> rate and extent <str<strong>on</strong>g>of</str<strong>on</strong>g> this invasi<strong>on</strong> (Ayres et al. 2004).Ma<str<strong>on</strong>g>the</str<strong>on</strong>g>matical models are a useful tool for investigating <str<strong>on</strong>g>the</str<strong>on</strong>g>relative importance <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>se mechanisms. In this paper weoutline <str<strong>on</strong>g>the</str<strong>on</strong>g> modeling approach used to describe <str<strong>on</strong>g>the</str<strong>on</strong>g>dynamics <str<strong>on</strong>g>of</str<strong>on</strong>g> this hybridizati<strong>on</strong>. We use <str<strong>on</strong>g>the</str<strong>on</strong>g> model to testhow increased vegetative growth rate, seedling survival andpollen producti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> hybrids affect <str<strong>on</strong>g>the</str<strong>on</strong>g> rate <str<strong>on</strong>g>of</str<strong>on</strong>g> populati<strong>on</strong>expansi<strong>on</strong> in areas <str<strong>on</strong>g>of</str<strong>on</strong>g> high and low recruitment. We find thatdepending <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> level <str<strong>on</strong>g>of</str<strong>on</strong>g> local recruitment, increasedvegetative growth rate or seedling survival <str<strong>on</strong>g>of</str<strong>on</strong>g> hybrids canresult in super-exp<strong>on</strong>ential populati<strong>on</strong> growth. Elevatedhybrid pollen producti<strong>on</strong> al<strong>on</strong>e results in an increase in <str<strong>on</strong>g>the</str<strong>on</strong>g>frequency <str<strong>on</strong>g>of</str<strong>on</strong>g> hybrids in <str<strong>on</strong>g>the</str<strong>on</strong>g> populati<strong>on</strong>, but does not predictsuper-exp<strong>on</strong>ential growth unless coupled with elevatedhybrid growth rate or seedling survival.MODEL AND METHODSHere we outline <str<strong>on</strong>g>the</str<strong>on</strong>g> key modeling assumpti<strong>on</strong>s andsketch <str<strong>on</strong>g>the</str<strong>on</strong>g> derivati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> model. The derivati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> fullquantitative genetic, integro-difference equati<strong>on</strong> model isFig. 1: super-exp<strong>on</strong>ential (bold line) vs exp<strong>on</strong>ential (dashed line) populati<strong>on</strong>growth. After a sufficiently l<strong>on</strong>g time, <str<strong>on</strong>g>the</str<strong>on</strong>g> area occupied by aninvasive growing super-exp<strong>on</strong>entially differs from an exp<strong>on</strong>entiallygrowing populati<strong>on</strong> by orders <str<strong>on</strong>g>of</str<strong>on</strong>g> magnitude.- 117 -