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 SpreadTHE INFLUENCE OF INTERTIDAL ZONE AND NATIVE VEGETATION ON THE SURVIVALAND GROWTH OF SPARTINA ANGLICA IN NORTHERN PUGET SOUND, WA, USAC. E. HELLQUIST 1 AND R. A. BLACKSchool <str<strong>on</strong>g>of</str<strong>on</strong>g> Biological Sciences, Washingt<strong>on</strong> State University, Pullman WA, 991641 Current address: Department <str<strong>on</strong>g>of</str<strong>on</strong>g> Biological Sciences, State University <str<strong>on</strong>g>of</str<strong>on</strong>g> New York, Oswego, NY 13126;eric.hellquist@oswego.eduSpartina anglica col<strong>on</strong>izes mudflats, tidal channels, salt marshes, and gravel beaches in nor<str<strong>on</strong>g>the</str<strong>on</strong>g>rnPuget Sound, Washingt<strong>on</strong>, USA. We measured Spartina seedling survival and growth al<strong>on</strong>g anintertidal gradient from mudflat to salt marsh at Alice Bay, Skagit County, Washingt<strong>on</strong>. Spartinaseedlings were transplanted into plots with full and reduced competiti<strong>on</strong> in open mudflat, a lowmarsh intertidal z<strong>on</strong>e dominated by Salicornia virginica, and a middle marsh z<strong>on</strong>e dominated byDistichlis spicata. In <str<strong>on</strong>g>the</str<strong>on</strong>g> mudflat, where little native vegetati<strong>on</strong> was present, two separate treatmentswere m<strong>on</strong>itored: unmanipulated (in situ) seedlings and seedlings transplanted within <str<strong>on</strong>g>the</str<strong>on</strong>g> mudflat.The in situ seedlings had 100% survival whereas seedlings transplanted within <str<strong>on</strong>g>the</str<strong>on</strong>g> mudflat had 60%survival. The mean relative growth rate (RGR) <str<strong>on</strong>g>of</str<strong>on</strong>g> in situ seedlings in <str<strong>on</strong>g>the</str<strong>on</strong>g> mudflat was 16 milligramsper milligram per day (mg mg -1 day -1 ) compared to RGR <str<strong>on</strong>g>of</str<strong>on</strong>g> 8 mg mg -1 day -1 for <str<strong>on</strong>g>the</str<strong>on</strong>g> transplantedseedlings. In <str<strong>on</strong>g>the</str<strong>on</strong>g> Salicornia virginica z<strong>on</strong>e, Spartina survival was 94% and RGR averaged 13 mgmg -1 day -1 with reduced competiti<strong>on</strong>. Spartina seedling survival was 90% and mean RGR was 11 mgmg -1 day -1 when grown in full competiti<strong>on</strong> with Salicornia. In <str<strong>on</strong>g>the</str<strong>on</strong>g> Distichlis z<strong>on</strong>e, Spartina survivalwas 57% and <str<strong>on</strong>g>the</str<strong>on</strong>g> RGR was 5 mg mg -1 day -1 without competiti<strong>on</strong>. Spartina seedling survivorship waszero when grown in competiti<strong>on</strong> with Distichlis. In general, Spartina survival and RGR were highestat lower intertidal elevati<strong>on</strong>s and with reduced competiti<strong>on</strong>. The spread <str<strong>on</strong>g>of</str<strong>on</strong>g> S. anglica into upperintertidal levels appears limited by competiti<strong>on</strong> as well as physical c<strong>on</strong>diti<strong>on</strong>s al<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> intertidalgradient.Keywords: competiti<strong>on</strong>, Distichlis spicata, Salicornia virginica, Spartina anglica, z<strong>on</strong>ati<strong>on</strong>INTRODUCTIONVegetati<strong>on</strong> z<strong>on</strong>ati<strong>on</strong> in salt marshes is determined byboth competitive (Bertness 1991a; Pennings and Callaway1992) and facilitative (Bertness and Shumway 1993,Bertness and Hacker 1994; Callaway and Pennings 2000)biotic interacti<strong>on</strong>s as well as physical c<strong>on</strong>diti<strong>on</strong>s includingsoil waterlogging, oxygen availability (Howes et al. 1981),sulfide toxicity (King et al. 1982) and porewater salinity(Callaway et al. 1990, Pennings and Callaway 1992). Innorthwestern Washingt<strong>on</strong>, salt marsh communities <str<strong>on</strong>g>of</str<strong>on</strong>g>tenform a fringe <str<strong>on</strong>g>of</str<strong>on</strong>g> vegetati<strong>on</strong> al<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> upper edges <str<strong>on</strong>g>of</str<strong>on</strong>g>mudflats. These sites have high porewater salinities (>30grams per kilogram [g kg -1 ) and are typically isolated fromriverine freshwater. The lowest intertidal z<strong>on</strong>es in <str<strong>on</strong>g>the</str<strong>on</strong>g>semarshes are typically col<strong>on</strong>ized by mats <str<strong>on</strong>g>of</str<strong>on</strong>g> Salicorniavirginica with intermittent patches <str<strong>on</strong>g>of</str<strong>on</strong>g> Spergulariacanadensis, Triglochin maritimum, and Puccinelliamaritima. Frequently, individuals <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>se species willcol<strong>on</strong>ize <str<strong>on</strong>g>the</str<strong>on</strong>g> open mudflat several meters <str<strong>on</strong>g>of</str<strong>on</strong>g>f <str<strong>on</strong>g>the</str<strong>on</strong>g> seawardedge <str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>tiguous salt marsh.The introducti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina anglica into northwesternWashingt<strong>on</strong> has altered <str<strong>on</strong>g>the</str<strong>on</strong>g> z<strong>on</strong>ati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> salt marsh vegetati<strong>on</strong>by creating a community <str<strong>on</strong>g>of</str<strong>on</strong>g> emergent vegetati<strong>on</strong> below <str<strong>on</strong>g>the</str<strong>on</strong>g>Salicornia virginica z<strong>on</strong>e <strong>on</strong> sediment that was previouslyopen mudflat. Throughout nor<str<strong>on</strong>g>the</str<strong>on</strong>g>rn Puget Sound, Spartinacan form dense stands in areas that were formerly open mudflats (e.g. Triangle Cove and Livingst<strong>on</strong> Bay, IslandCounty). However, Spartina is <strong>on</strong>ly found sporadicallygrowing am<strong>on</strong>g native plants in higher intertidal z<strong>on</strong>es (e.g.at Maylor Marsh and English Boom, Island County).Based <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> tendency <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina to col<strong>on</strong>ize openmudflats as opposed to closed mats <str<strong>on</strong>g>of</str<strong>on</strong>g> native vegetati<strong>on</strong>, wehypo<str<strong>on</strong>g>the</str<strong>on</strong>g>sized that Spartina is an inferior competitor and thatsurvival and growth rates would be highest in <str<strong>on</strong>g>the</str<strong>on</strong>g> lowestintertidal z<strong>on</strong>es and in experimental plots where competiti<strong>on</strong>from native plants was limited.MATERIALS AND METHODSWe c<strong>on</strong>ducted a seedling transplant experiment in fourlocati<strong>on</strong>s at Alice Bay (48º 33’ 20” N, 122º 29’11” W;Skagit County). A series <str<strong>on</strong>g>of</str<strong>on</strong>g> 10 random plots were placedal<strong>on</strong>g 30-meter (m) transects in <str<strong>on</strong>g>the</str<strong>on</strong>g> mudflat. We alsom<strong>on</strong>itored <str<strong>on</strong>g>the</str<strong>on</strong>g> growth <str<strong>on</strong>g>of</str<strong>on</strong>g> 10 naturally occurring,unmanipulated (in situ) seedlings in <str<strong>on</strong>g>the</str<strong>on</strong>g> mudflat to c<strong>on</strong>trolfor <str<strong>on</strong>g>the</str<strong>on</strong>g> effects <str<strong>on</strong>g>of</str<strong>on</strong>g> transplanting. Ten paired plots were-99-