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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 3: Ecosystem Effects <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>Invasive</strong> SpartinaIMPACTS OF BENTHIC INVERTEBRATES ON SEDIMENT POREWATER AMMONIUM ANDSULFIDE:CONSEQUENCES FOR SPARTINA SEEDLING GROWTHU.H. MAHL 1,2 ,A.C.TYLER 1,3 AND E.D. GROSHOLZ 11 Department <str<strong>on</strong>g>of</str<strong>on</strong>g> Envir<strong>on</strong>mental Science and Policy, University <str<strong>on</strong>g>of</str<strong>on</strong>g> California, Davis, CA 956162 Current address: Department <str<strong>on</strong>g>of</str<strong>on</strong>g> Biology, University <str<strong>on</strong>g>of</str<strong>on</strong>g> Notre Dame, South Bend, IN 46556; umahl@nd.edu3 Current address: School <str<strong>on</strong>g>of</str<strong>on</strong>g> Biological and Medical Sciences, Rochester Institute <str<strong>on</strong>g>of</str<strong>on</strong>g> Technology, Rochester, NY 14623Since its introducti<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g> 1970s, Spartina alterniflora and its hybrids have rapidly invaded <str<strong>on</strong>g>the</str<strong>on</strong>g>intertidal z<strong>on</strong>e <str<strong>on</strong>g>of</str<strong>on</strong>g> San Francisco Bay. We know relatively little about <str<strong>on</strong>g>the</str<strong>on</strong>g> biotic and abiotic factorsthat have ei<str<strong>on</strong>g>the</str<strong>on</strong>g>r facilitated or hindered this invasi<strong>on</strong>. In its native range, nitrogen availability andsediment anoxia are known to limit <str<strong>on</strong>g>the</str<strong>on</strong>g> growth <str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora. Benthic invertebrates may alterporewater c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> both amm<strong>on</strong>ium and soluble sulfide, and <str<strong>on</strong>g>the</str<strong>on</strong>g>reby indirectly influence S.alterniflora success. In order to better understand how <str<strong>on</strong>g>the</str<strong>on</strong>g> resident macr<str<strong>on</strong>g>of</str<strong>on</strong>g>aunal invertebratecommunity may impact <str<strong>on</strong>g>the</str<strong>on</strong>g> expansi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora into <str<strong>on</strong>g>the</str<strong>on</strong>g> intertidal z<strong>on</strong>e, we examined howcomm<strong>on</strong> invertebrates influence c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> amm<strong>on</strong>ium and soluble sulfide in sedimentporewater. We c<strong>on</strong>ducted laboratory microcosm experiments to determine how species from threefuncti<strong>on</strong>al feeding groups <str<strong>on</strong>g>of</str<strong>on</strong>g> benthic invertebrates (subsurface deposit feeders, surface depositfeeders and surface grazers) affect porewater in unvegetated areas adjacent to Spartina-invadedareas. In a separate experiment, we examined <str<strong>on</strong>g>the</str<strong>on</strong>g> growth <str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora seedlings in <str<strong>on</strong>g>the</str<strong>on</strong>g> presence<str<strong>on</strong>g>of</str<strong>on</strong>g> individual invertebrates. Relative to microcosms without invertebrates, where porewateramm<strong>on</strong>ium was fairly high (greater than 400 micromoles per liter [μM]), we found slightly lowerporewater amm<strong>on</strong>ium in microcosms with Heteromastus filiformis (subsurface deposit feeder) orMacoma petalum (surface deposit feeder). Porewater sulfide was slightly higher in <str<strong>on</strong>g>the</str<strong>on</strong>g> presence <str<strong>on</strong>g>of</str<strong>on</strong>g>H. filiformis <strong>on</strong>ly. The significantly greater growth <str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora seedlings in <str<strong>on</strong>g>the</str<strong>on</strong>g> presence <str<strong>on</strong>g>of</str<strong>on</strong>g> M.petalum than in <str<strong>on</strong>g>the</str<strong>on</strong>g> presence <str<strong>on</strong>g>of</str<strong>on</strong>g> H. filiformis suggests that both high sulfide and high amm<strong>on</strong>iummay have been detrimental to seedling success. Thus, invertebrates may indirectly influence <str<strong>on</strong>g>the</str<strong>on</strong>g>success <str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora seedlings by altering porewater chemistry.Keywords: amm<strong>on</strong>ium, benthic, functi<strong>on</strong>al group, invasive species, porewater, Spartina, sulfideINTRODUCTIONAm<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> greatest threats to natural ecosystems areinvasi<strong>on</strong>s by n<strong>on</strong>-native species (Drake et al. 1989;Vitousek et al. 1997). However, <str<strong>on</strong>g>the</str<strong>on</strong>g> mechanisms thatdetermine <str<strong>on</strong>g>the</str<strong>on</strong>g> success or failure <str<strong>on</strong>g>of</str<strong>on</strong>g> new invasi<strong>on</strong>s are <str<strong>on</strong>g>of</str<strong>on</strong>g>tenpoorly understood. The invasi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> Pacific Coast estuariesby Spartina alterniflora and its hybrids (S. alterniflora xnative Spartina foliosa) provides some insight into howSpartina can rapidly change benthic communities throughaltering physico-chemical properties <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> habitat. Theshift from native mudflats and relatively diverse uppermarsh habitats to dense Spartina meadows followinginvasi<strong>on</strong> has pr<str<strong>on</strong>g>of</str<strong>on</strong>g>ound effects <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> functi<strong>on</strong>al diversity <str<strong>on</strong>g>of</str<strong>on</strong>g>benthic invertebrates, nutrient cycling, and o<str<strong>on</strong>g>the</str<strong>on</strong>g>r physicalprocesses (Neira et al. 2005, 2006; Levin et al. 2006).However, we still have little informati<strong>on</strong> <strong>on</strong> what biotic andabiotic factors may c<strong>on</strong>tribute to <str<strong>on</strong>g>the</str<strong>on</strong>g> great success <str<strong>on</strong>g>of</str<strong>on</strong>g>Spartina in <str<strong>on</strong>g>the</str<strong>on</strong>g> intertidal z<strong>on</strong>e <str<strong>on</strong>g>of</str<strong>on</strong>g> San Francisco Bay.Determining which factors most str<strong>on</strong>gly influence seedlingestablishment will greatly improve our understanding <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>dynamics <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> invasi<strong>on</strong>.Previous work has shown that nutrient limitati<strong>on</strong> andanoxia affect <str<strong>on</strong>g>the</str<strong>on</strong>g> growth and survival <str<strong>on</strong>g>of</str<strong>on</strong>g> native S.alterniflora in Atlantic coast salt marshes (e.g., Gallagher1975; King et al. 1982; DeLaune et al. 1983; Dai andWiegert 1997) and that nutrient limitati<strong>on</strong> may be especiallysevere during <str<strong>on</strong>g>the</str<strong>on</strong>g> early stages <str<strong>on</strong>g>of</str<strong>on</strong>g> marsh development in bothnative and invaded marshes (Tyler et al. 2003, 2007).Benthic invertebrates can significantly impact <str<strong>on</strong>g>the</str<strong>on</strong>g>c<strong>on</strong>centrati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> solutes in porewater and nutrient cyclingthrough bioturbati<strong>on</strong>, burrow ventilati<strong>on</strong> and c<strong>on</strong>sumpti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g>organic matter (e.g. Aller 1982, Peters<strong>on</strong> and Heck 1999;Christensen et al. 2000). However, research has not beend<strong>on</strong>e to determine whe<str<strong>on</strong>g>the</str<strong>on</strong>g>r <str<strong>on</strong>g>the</str<strong>on</strong>g> effects <str<strong>on</strong>g>of</str<strong>on</strong>g> benthiccommunities <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> c<strong>on</strong>centrati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> nutrients (e.g.,amm<strong>on</strong>ium) and toxic metabolites (e.g., soluble sulfide) inporewater can affect <str<strong>on</strong>g>the</str<strong>on</strong>g> success <str<strong>on</strong>g>of</str<strong>on</strong>g> invasive plants like S.alterniflora.As part <str<strong>on</strong>g>of</str<strong>on</strong>g> an investigati<strong>on</strong> linking benthic communitystructure to <str<strong>on</strong>g>the</str<strong>on</strong>g> establishment <str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora seedlings, weperformed two pilot microcosm experiments. The objective<str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> first experiment was to determine whe<str<strong>on</strong>g>the</str<strong>on</strong>g>r comm<strong>on</strong>benthic invertebrates from three different functi<strong>on</strong>al feeding- 165 -

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