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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 4: Spartina C<strong>on</strong>trol and Managementmaintain elevated sediments and altered biogeochemicalprocesses (Fig. 2A, left side). Active water movement and<str<strong>on</strong>g>the</str<strong>on</strong>g> scouring acti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> shifting cobbles and gravel shouldhamper this process. Ultimately, we predict that analternative state will not be maintained due to <str<strong>on</strong>g>the</str<strong>on</strong>g> transiti<strong>on</strong>alprocess <str<strong>on</strong>g>of</str<strong>on</strong>g> water movement increasing sediment erosi<strong>on</strong>around plant roots and decreasing subsequent vascular plantand infaunal recruitment. As a result, negative feedbackprocesses in <str<strong>on</strong>g>the</str<strong>on</strong>g> maintenance comp<strong>on</strong>ent <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> alternativestate will shift cobble beach community structure to arestored state (Fig. 2A, right side). Algal recruitment willincrease as sediment erosi<strong>on</strong> occurs and cobbles re-emerge,pushing <str<strong>on</strong>g>the</str<strong>on</strong>g> community into a positive feedback loop thatincludes loss <str<strong>on</strong>g>of</str<strong>on</strong>g> sediment, decreased native vascular plantrecruitment, and c<strong>on</strong>tinued increases in algal and infaunalrecruitment (Fig. 2A, right side).We hypo<str<strong>on</strong>g>the</str<strong>on</strong>g>size that mudflat habitats, because <str<strong>on</strong>g>the</str<strong>on</strong>g>yexperience lower wave acti<strong>on</strong>, will have increased vascularplant recruitment, and allow for <str<strong>on</strong>g>the</str<strong>on</strong>g> maintenance <str<strong>on</strong>g>of</str<strong>on</strong>g>cordgrass sediment accreti<strong>on</strong> and biogeochemical processes(Fig. 2A, left side). We expect that a positive feedback loopgenerated by slower water movement and <str<strong>on</strong>g>the</str<strong>on</strong>g> presence <str<strong>on</strong>g>of</str<strong>on</strong>g>vascular plants will maintain sediment characteristicscreated by cordgrass, decrease algal and infaunalrecruitment, and c<strong>on</strong>tinue to increase native vascular plantrecruitment (Fig. 2A, left side).Finally, we suggest that high and low salinity marshespreviously invaded by cordgrass will experience recruitment<str<strong>on</strong>g>of</str<strong>on</strong>g> higher intertidal vascular plant assemblages, ra<str<strong>on</strong>g>the</str<strong>on</strong>g>r than<str<strong>on</strong>g>the</str<strong>on</strong>g> original assemblage, due to <str<strong>on</strong>g>the</str<strong>on</strong>g> increased tidal elevati<strong>on</strong>produced by cordgrass-accreted sediments. We expect that<str<strong>on</strong>g>the</str<strong>on</strong>g>se plants will be good at maintaining sediment depth andbiogeochemical processes originally created by cordgrass.Their presence will be maintained via a positive feedbackloop that increases <str<strong>on</strong>g>the</str<strong>on</strong>g>ir own c<strong>on</strong>tinued recruitment whiledecreasing that <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> lower intertidal plant communitypresent before <str<strong>on</strong>g>the</str<strong>on</strong>g> invasi<strong>on</strong> (Fig. 2B, left side). However, ifwater movement is sufficient to erode sediments or if plantrecruitment is low or delayed, marsh communities may shiftinto a restored state (Fig. 2B, right side).Testing <str<strong>on</strong>g>the</str<strong>on</strong>g>se hypo<str<strong>on</strong>g>the</str<strong>on</strong>g>ses will require both large andsmall-scale experiments in areas where cordgrass has beenremoved. Ultimately, this research will provide natural areamanagers with better ways <str<strong>on</strong>g>of</str<strong>on</strong>g> predicting and evaluating <str<strong>on</strong>g>the</str<strong>on</strong>g>c<strong>on</strong>sequences <str<strong>on</strong>g>of</str<strong>on</strong>g> post-removal impact across differenthabitat types. It may be that active removal <str<strong>on</strong>g>of</str<strong>on</strong>g> nativevascular plant assemblages will be necessary in habitats suchas mudflats where restorati<strong>on</strong> could be c<strong>on</strong>tinually hinderedby <str<strong>on</strong>g>the</str<strong>on</strong>g> recruitment and positive feedbacks produced by <str<strong>on</strong>g>the</str<strong>on</strong>g>seplants. Although invasive species removal and restorati<strong>on</strong> isa critical comp<strong>on</strong>ent to <str<strong>on</strong>g>the</str<strong>on</strong>g> management <str<strong>on</strong>g>of</str<strong>on</strong>g> many naturalareas, most research is site or species-specific. The proposedresearch will help establish <str<strong>on</strong>g>the</str<strong>on</strong>g> importance <str<strong>on</strong>g>of</str<strong>on</strong>g> a general<str<strong>on</strong>g>the</str<strong>on</strong>g>ory <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> c<strong>on</strong>textual dependence <str<strong>on</strong>g>of</str<strong>on</strong>g> invasive speciesremoval that can be applied to communities with varyingspecies assemblages, physical c<strong>on</strong>diti<strong>on</strong>s, and degrees <str<strong>on</strong>g>of</str<strong>on</strong>g>invasi<strong>on</strong>.ACKNOWLEDGEMENTSWe thank <str<strong>on</strong>g>the</str<strong>on</strong>g> many hands that assisted with <str<strong>on</strong>g>the</str<strong>on</strong>g> researchincluding C. Catt<strong>on</strong>, C. Gozart, E. Hellquist, A. Hysert, T.Reeder, T. Riord<strong>on</strong>, and T. Royce. The research wassupported by Washingt<strong>on</strong> and Nati<strong>on</strong>al Sea Grant Programs.REFERENCESBruno, J., and M.D. Bertness. 2001. Habitat modificati<strong>on</strong> andfacilitati<strong>on</strong> in benthic marine communities. Pages 201-220 In:M.D. Bertness, S.D. Gaines, and M.E. Hay, eds., MarineCommunity Ecology. Sinauer Associates: Sunderland, MA, pp.201-210.Crooks, J. 2002. Characterizing ecosystem-level c<strong>on</strong>sequences <str<strong>on</strong>g>of</str<strong>on</strong>g>biological invasi<strong>on</strong>s: <str<strong>on</strong>g>the</str<strong>on</strong>g> role <str<strong>on</strong>g>of</str<strong>on</strong>g> ecosystem engineers. Oikos97:153-166.D’Ant<strong>on</strong>io, C.D., and L.A. Meyers<strong>on</strong>. 2002. Exotic plant species asproblems and soluti<strong>on</strong>s in ecological restorati<strong>on</strong>: a syn<str<strong>on</strong>g>the</str<strong>on</strong>g>sis.Restorati<strong>on</strong> Ecology 10:703–713.Daehler, C.C., and D.R. Str<strong>on</strong>g. 1996. Status, predicti<strong>on</strong> andpreventi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> introduced cordgrass, Spartina spp. invasi<strong>on</strong>s inPacific estuaries, USA. Biological C<strong>on</strong>servati<strong>on</strong> 78:51-58.Dethier, M.N., and S.D. Hacker. 2005. Physical factors vs. bioticresistance in c<strong>on</strong>trolling <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> an estuarine marsh grass.Ecological Applicati<strong>on</strong>s 15:1273-1283.Dethier, M.N., and S.D. Hacker. 2004. Improving managementpractices for invasive cordgrass in <str<strong>on</strong>g>the</str<strong>on</strong>g> Pacific Northwest: a casestudy <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina anglica. Washingt<strong>on</strong> Sea Grant Publicati<strong>on</strong>s,Seattle, WA, USA.Goss-Custard, J.D., and M.E. Moser. 1988. Rates <str<strong>on</strong>g>of</str<strong>on</strong>g> change in <str<strong>on</strong>g>the</str<strong>on</strong>g>numbers <str<strong>on</strong>g>of</str<strong>on</strong>g> Dunlin, Calidris alpina, wintering in British estuariesin relati<strong>on</strong> to <str<strong>on</strong>g>the</str<strong>on</strong>g> spread <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina anglica. Journal <str<strong>on</strong>g>of</str<strong>on</strong>g> AppliedEcology 25:95-109.Grosholz, E. 2002. Ecological and evoluti<strong>on</strong>ary c<strong>on</strong>sequences <str<strong>on</strong>g>of</str<strong>on</strong>g>coastal invasi<strong>on</strong>s. Trends in Ecology and Evoluti<strong>on</strong> 17:22–27.Hacker, S.D., and M.N. Dethier. 2006. Community modificati<strong>on</strong> bya grass invader has differing impacts for marine habitats. Oikos113:279-286.Hacker, S.D., and M.N. Dethier. 2009. Differing c<strong>on</strong>sequences <str<strong>on</strong>g>of</str<strong>on</strong>g>removing ecosystem-modifying invaders: Significance <str<strong>on</strong>g>of</str<strong>on</strong>g> impactand community c<strong>on</strong>text to restorati<strong>on</strong> potential. In: J.A. Rilovand J.A. Crooks, eds., Biological Invasi<strong>on</strong>s in MarineEcosystems. Springer-Verlag: Berlin Heidelberg, pp. 375-385.Hacker, S.D., D. Heimer, C.E. Hellquist, T.G. Reeder, B. Reeves,T. Riordan, and M.N. Dethier. 2001. A marine plant (Spartinaanglica) invades widely varying habitats: potential mechanisms<str<strong>on</strong>g>of</str<strong>on</strong>g> invasi<strong>on</strong> and c<strong>on</strong>trol. Biological Invasi<strong>on</strong>s 3:211-217.Hobbs, R.J., and S.E. Humphries. 1995. An integrated approach to<str<strong>on</strong>g>the</str<strong>on</strong>g> ecology and management <str<strong>on</strong>g>of</str<strong>on</strong>g> plant invasi<strong>on</strong>s. C<strong>on</strong>servati<strong>on</strong>Biology 9:761–770.J<strong>on</strong>es, C.G., J.H. Lawt<strong>on</strong>, and M. Shachak. 1994. Organisms asecosystem engineers. Oikos 689:373-386.Lewint<strong>on</strong>, R.C. 1969. The meaning <str<strong>on</strong>g>of</str<strong>on</strong>g> stability. In: Diversity andstability in ecological systems. Brookhaven Symposia in BiologyNo. 22. Brookhaven Nati<strong>on</strong>al Laboratories, Brookhaven, NY,USA, pp. 13-24.Maricle, B.R., and R.W. Lee. 2002. Aerenchyma development andoxygen transport in <str<strong>on</strong>g>the</str<strong>on</strong>g> estuarine cordgrasses Spartinaalterniflora and S. anglica. Aquatic Botany 74:109-120.Myers, J.H., D. Simberl<str<strong>on</strong>g>of</str<strong>on</strong>g>f, A.M. Kuris, and J.R. Carey. 2000.Eradicati<strong>on</strong> revisited: dealing with exotic species. Trends inEcology and Evoluti<strong>on</strong> 15:316-320.- 215 -

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