<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> SpartinaMECHANISTIC PROCESSES DRIVING SHIFTS IN BENTHIC INFAUNAL COMMUNITIESFOLLOWING HYBRID SPARTINA TIDAL FLAT INVASIONC. NEIRA 1 , E.D. GROSHOLZ 2 AND L.A. LEVIN 31 Integrative Oceanography Divisi<strong>on</strong>, Scripps Instituti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> Oceanography, La Jolla, California 92093-0218, USA;cneira@coast.ucsd.edu2 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, One Shields Ave., Davis, CA 95616,USA; tedgrosholz@ucdavis.edu3 Integrative Oceanography Divisi<strong>on</strong>, Scripps Instituti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> Oceanography, La Jolla, California 92093-0218, USA;llevin@ucsd.eduSpartina alterniflora x foliosa hybrids are perennial cordgrasses that have rapidly invaded mudflatsand marshes in central and sou<str<strong>on</strong>g>the</str<strong>on</strong>g>rn San Francisco Bay. Recent studies c<strong>on</strong>ducted by <str<strong>on</strong>g>the</str<strong>on</strong>g> authors at<str<strong>on</strong>g>the</str<strong>on</strong>g> Elsie Roemer Bird Sanctuary in Alameda (San Francisco Bay) showed a 75% reducti<strong>on</strong> inmacr<str<strong>on</strong>g>of</str<strong>on</strong>g>aunal densities and shift in macr<str<strong>on</strong>g>of</str<strong>on</strong>g>aunal compositi<strong>on</strong>. Here we identify <str<strong>on</strong>g>the</str<strong>on</strong>g> mechanisms thatunderlie such observed changes in macr<str<strong>on</strong>g>of</str<strong>on</strong>g>aunal community structure following tidal flat invasi<strong>on</strong> by<str<strong>on</strong>g>the</str<strong>on</strong>g> hybrid Spartina. Specifically we performed a series <str<strong>on</strong>g>of</str<strong>on</strong>g> in situ manipulative experiments toexamine hybrid Spartina canopy influence <strong>on</strong> water moti<strong>on</strong> and water flow speed, larval flux,animal transport, and predati<strong>on</strong>, as mediators <str<strong>on</strong>g>of</str<strong>on</strong>g> change for sediments and macrobenthos. Overall,hybrid Spartina exerted a str<strong>on</strong>g influence <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> hydrodynamic regime, reducing water flow that, inturn, influences flux <str<strong>on</strong>g>of</str<strong>on</strong>g> recruiting larvae, transport <str<strong>on</strong>g>of</str<strong>on</strong>g> o<str<strong>on</strong>g>the</str<strong>on</strong>g>r benthos, and <str<strong>on</strong>g>the</str<strong>on</strong>g> input <str<strong>on</strong>g>of</str<strong>on</strong>g> organic matterand sediment depositi<strong>on</strong>. Habitat modificati<strong>on</strong> results in poor survivorship <str<strong>on</strong>g>of</str<strong>on</strong>g> surface-feeding taxavia sulfide toxicity, altered predati<strong>on</strong> pressure and changed food availability. All <str<strong>on</strong>g>the</str<strong>on</strong>g>se mechanismscan play key, possibly synergistic roles in structuring Spartina-invaded ecosystems.Keywords: tidal flat invasi<strong>on</strong>, Spartina alterniflora, hybrid Spartina, benthos, macr<str<strong>on</strong>g>of</str<strong>on</strong>g>auna,mechanistic processesINTRODUCTIONSan Francisco Bay is <strong>on</strong>e <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> most heavily invadedestuaries in <str<strong>on</strong>g>the</str<strong>on</strong>g> world with nearly 250 n<strong>on</strong>-native orintroduced species (Cohen and Carlt<strong>on</strong> 1998). One <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>most serious invasi<strong>on</strong>s has been that <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> Atlanticcordgrass Spartina alterniflora and its hybrids (hereafter“hybrid Spartina”). The genetic background <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> plantswas c<strong>on</strong>firmed by molecular genetic analysis by D. Ayres(unpublished results). Hybrid Spartina has invaded morethan 800 hectares (ha) <str<strong>on</strong>g>of</str<strong>on</strong>g> mudflats and marshes in centraland south San Francisco Bay (Ayres et al. 2004). Thisinvasive cordgrass is c<strong>on</strong>verting mudflats at low tidal levelsinto dense, nearly m<strong>on</strong>otypic meadows (Ayres et al. 2003,2004). Of extreme c<strong>on</strong>cern is that this plant’s invasi<strong>on</strong> intounvegetated tidal flats will result in a loss <str<strong>on</strong>g>of</str<strong>on</strong>g> open foragingarea for shorebirds and fishes, flow reducti<strong>on</strong>s, highersedimentati<strong>on</strong> rates, changes in light penetrati<strong>on</strong>, andreducti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> benthic algal producti<strong>on</strong> (Zipperer 1996;Daehler and Str<strong>on</strong>g 1996; Stenzel et al. 2002; Grosholz et al.2009).To date very little is known about <str<strong>on</strong>g>the</str<strong>on</strong>g> impact <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>hybrid Spartina invasi<strong>on</strong> <strong>on</strong> sediment properties,macr<str<strong>on</strong>g>of</str<strong>on</strong>g>aunal communities, and ecosystem functi<strong>on</strong>ing. Whatwe do know results from recent studies <str<strong>on</strong>g>of</str<strong>on</strong>g> three sites in SanFrancisco Bay, including <str<strong>on</strong>g>the</str<strong>on</strong>g> Elsie Roemer Bird Sanctuary inAlameda (San Francisco Bay, CA, USA) (Neira et al. 2005),which has experienced hybrid Spartina invasi<strong>on</strong> for <str<strong>on</strong>g>the</str<strong>on</strong>g> past30 years. At this site macr<str<strong>on</strong>g>of</str<strong>on</strong>g>aunal densities were 75% lowerin hybrid Spartina-invaded sediments than <strong>on</strong> adjacent,uninvaded tidal flats (Neira et al. 2005). Biomass was 57%lower in invaded sediments (Levin et al. 2006). We alsoobserved important shifts in species compositi<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g>hybrid-invaded patches relative to tidal flats (Neira et al.2005). Surface feeders such as Gemma gemma (Bivalvia),Corophium spp. and Grandidierella jap<strong>on</strong>ica (Amphipoda),and Tharyx sp. and Ete<strong>on</strong>e sp. (Polychaeta) were negativelyaffected by Spartina invasi<strong>on</strong>, exhibiting reduced densities.Subsurface-deposit feeders such as capitellid polychaetesand tubificid oligochaetes were less affected or unaffected(Neira et al. 2005). Because surface-feeding taxa are moreaccessible to epibenthic c<strong>on</strong>sumers than capitellidpolychaetes and oligochaetes that live deeper in <str<strong>on</strong>g>the</str<strong>on</strong>g>sediment, <str<strong>on</strong>g>the</str<strong>on</strong>g> loss <str<strong>on</strong>g>of</str<strong>on</strong>g> surface feeding taxa could havepr<str<strong>on</strong>g>of</str<strong>on</strong>g>ound implicati<strong>on</strong>s for higher trophic levels and henceaffect <str<strong>on</strong>g>the</str<strong>on</strong>g> whole ecosystem. Therefore, <str<strong>on</strong>g>the</str<strong>on</strong>g> aim <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>following work was to experimentally document <str<strong>on</strong>g>the</str<strong>on</strong>g> causes<str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> benthic changes identified in <str<strong>on</strong>g>the</str<strong>on</strong>g> initial mensurativestudy.METHODSThe study site was located <strong>on</strong> Alameda Island (SanFrancisco Bay) al<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> shoreline adjacent to Elsie RoemerBird Sanctuary (37 o 45’35”N; 122 o 28’48”W). Detailed- 141 -
Chapter 3: Ecosystem Effects <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>Invasive</strong> Spartina<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> Spartinadescripti<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> study site is provided in Neira et al.(2005). Using a paired sampling design, we established 10blocks (2x2 meters (m)), approximately 10 m inside <str<strong>on</strong>g>the</str<strong>on</strong>g>hybrid Spartina meadow, and 10 similar blocks <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g>adjacent open tidal flat approximately 5-10 m from <str<strong>on</strong>g>the</str<strong>on</strong>g>meadow edge. We performed in situ manipulativeexperiments to identify what mechanisms are resp<strong>on</strong>sible forobserved shifts in faunal community structure followinghybrid Spartina invasi<strong>on</strong>.Water moti<strong>on</strong>: To evaluate <str<strong>on</strong>g>the</str<strong>on</strong>g> influence <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> hybridSpartina canopy <strong>on</strong> relative water moti<strong>on</strong>, we used <str<strong>on</strong>g>the</str<strong>on</strong>g>gypsum dissoluti<strong>on</strong> technique (Doty 1971). Pre-weighedgypsum cards were deployed about 10 cm above <str<strong>on</strong>g>the</str<strong>on</strong>g> bottomfor 6, 3 and 4 days during April and June 2002 in vegetatedand unvegetated tidal flat habitats. It is assumed thatdissoluti<strong>on</strong> rate <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> gypsum, grams per day (g d -1 ), isproporti<strong>on</strong>al to water velocity (Porter et al. 2000). Watervelocity in both habitats was measured <strong>on</strong> several days nearmaximum ebb and flood tides just below <str<strong>on</strong>g>the</str<strong>on</strong>g> water surfacewith a Marsh-McBirney Flow Meter 2000.Larval flux: The influence <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> hybrid Spartinacanopy <strong>on</strong> larval flux was measured in vegetated andunvegetated habitats using Geukensia demissa (mussel)shells as a hard substrate for settlement. Barnacle larvalabundance over time was used as a proxy for larval flux.Three dowels, each with <strong>on</strong>e attached Geukensia shell, wereinserted into <str<strong>on</strong>g>the</str<strong>on</strong>g> sediment (1 m 2 plot) in each block <str<strong>on</strong>g>of</str<strong>on</strong>g> bothhybrid Spartina habitat and tidal flat (i.e., 60 in total).Mussels remained 10-20 cm above <str<strong>on</strong>g>the</str<strong>on</strong>g> sediment.Sediment depositi<strong>on</strong>: We investigated <str<strong>on</strong>g>the</str<strong>on</strong>g> effects <str<strong>on</strong>g>of</str<strong>on</strong>g>Spartina plant canopy <strong>on</strong> short-term sediment depositi<strong>on</strong>rates by deploying petri-dish sediment traps (Reed 1992) inboth vegetated and unvegetated habitats (10 replicates each)during low tide. Sediment traps were composed <str<strong>on</strong>g>of</str<strong>on</strong>g> GF/FWhatman filters (9-cm diameter) supported <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> petridishes affixed <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> sediment surface. Filters were removedand replaced 24 hours (h) later (<strong>on</strong>e tidal cycle) during twosuccessive days in July 2002. Filters were gently rinsed withdistilled water to remove salts <strong>on</strong> pre-weighed aluminumdishes, oven-dried at 60 o C, and re-weighed. Sedimentdepositi<strong>on</strong> rate was calculated as mass deposited per trap andexpressed in milligrams per centimeter squared per day (mgcm -2 d -1) . Percent organic matter was determined by massloss after igniti<strong>on</strong> at 500 o C for 4 h. Mud c<strong>on</strong>tent wasestimated after wet sieving (63 micrometers(μm)) <str<strong>on</strong>g>the</str<strong>on</strong>g>sediment deposited <strong>on</strong> traps and weighing both fracti<strong>on</strong>s (>63 μm and < 63 μm) after drying at 60°C.Animal transport: The influence <str<strong>on</strong>g>of</str<strong>on</strong>g> hybrid Spartinacanopy <strong>on</strong> animal-transport dynamics was evaluated usingpassive tube traps made <str<strong>on</strong>g>of</str<strong>on</strong>g> polypropylene (22 cm tall x 2.7cm diameter). To prevent escape <str<strong>on</strong>g>of</str<strong>on</strong>g> animals from <str<strong>on</strong>g>the</str<strong>on</strong>g> tube,15 milliliters (ml) <str<strong>on</strong>g>of</str<strong>on</strong>g> a dense brine soluti<strong>on</strong> (>90 parts perthousand (ppt)) was added; <str<strong>on</strong>g>the</str<strong>on</strong>g> remained volume was filledwith filtered seawater. Ten replicate tube traps weredeployed <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> unvegetated tidal flat about 10 cm above <str<strong>on</strong>g>the</str<strong>on</strong>g>sediment surface, supported <strong>on</strong> PVC pipe inserted into <str<strong>on</strong>g>the</str<strong>on</strong>g>sediment. In <str<strong>on</strong>g>the</str<strong>on</strong>g> hybrid Spartina habitat, tube traps wereinserted into <str<strong>on</strong>g>the</str<strong>on</strong>g> sediment leaving <str<strong>on</strong>g>the</str<strong>on</strong>g>ir opening about 5 cmabove <str<strong>on</strong>g>the</str<strong>on</strong>g> bottom. Sediment was collected from traps inplastic jars and preserved in 8% buffered formalin.Sediment properties: In order to explore how hybridSpartina ultimately affects <str<strong>on</strong>g>the</str<strong>on</strong>g> sediment ecosystem, weexamined some key sediment properties in vegetated andunvegetated habitats (10 replicates each). Porewater salinity(top 3 cm) was measured with a hand-held refractometer,sediment redox potential (top 1 cm) was measured with aportable Mettler Toledo redox meter. Plexi-glass cores (18.1cm 2 , 0-6 cm depth) were taken for total organic c<strong>on</strong>tent(determined after combusti<strong>on</strong> at 500°C x 4h); syringe coreswere taken for chlorophyll a (an estimate <str<strong>on</strong>g>of</str<strong>on</strong>g> sedimentmicroalgal biomass) and determined according to Plante-Cuny (1973) after extracti<strong>on</strong> with 90% acet<strong>on</strong>e. Sedimentporosity was determined according to Buchanan (1984).Porewater sulfide was measured c<strong>on</strong>currently by A.C. Tyler(UC Davis) based <strong>on</strong> Cline (1969) with a few modificati<strong>on</strong>s.Macr<str<strong>on</strong>g>of</str<strong>on</strong>g>auna were collected from both habitats with cores(18.1 cm 2 , 0-6 cm depth) and sieved through a 0.3-mm meshsieve.Plant removal experiment: We also performed anexperiment to determine if <str<strong>on</strong>g>the</str<strong>on</strong>g> invaded habitats would returnto <str<strong>on</strong>g>the</str<strong>on</strong>g> original unvegetated c<strong>on</strong>diti<strong>on</strong> and resembleunvegetated tidal flats. We clipped all above-groundSpartina plant material to <str<strong>on</strong>g>the</str<strong>on</strong>g> sediment level in ten replicate2x2 m areas with adjacent c<strong>on</strong>trols. In both removal andc<strong>on</strong>trols, we compared sediment properties and macr<str<strong>on</strong>g>of</str<strong>on</strong>g>aunalcommunities am<strong>on</strong>g habitats after 90 days.Sediment transplant experiment: We c<strong>on</strong>ducted atransplant experiment to determine whe<str<strong>on</strong>g>the</str<strong>on</strong>g>r unvegetatedsediment and fauna from <str<strong>on</strong>g>the</str<strong>on</strong>g> tidal flat would begin to looklike those in <str<strong>on</strong>g>the</str<strong>on</strong>g> invaded areas when moved into <str<strong>on</strong>g>the</str<strong>on</strong>g> areainvaded by hybrid Spartina. In summer 2002, intactsediment (625 cm 2 x 10 cm depth) was moved from <str<strong>on</strong>g>the</str<strong>on</strong>g> tidalflat (about 7 m from <str<strong>on</strong>g>the</str<strong>on</strong>g> edge) to Spartina-invaded habitat(10 m inside <str<strong>on</strong>g>the</str<strong>on</strong>g> meadow). Tidal flat sediment removed andreplaced served as a c<strong>on</strong>trol treatment. Each treatmentc<strong>on</strong>tained ten replicate blocks (20 in total).Predati<strong>on</strong>: In order to assess if <str<strong>on</strong>g>the</str<strong>on</strong>g> shifts observed inmacr<str<strong>on</strong>g>of</str<strong>on</strong>g>aunal compositi<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g> initial transplant experimentwere <str<strong>on</strong>g>the</str<strong>on</strong>g> result <str<strong>on</strong>g>of</str<strong>on</strong>g> changes in predati<strong>on</strong> pressure followingSpartina-hybrid invasi<strong>on</strong>, we performed c<strong>on</strong>trolled andreplicated in situ predator exclusi<strong>on</strong> experiments beginning<strong>on</strong> September 10, 2003. We used European green crabs(Carcinus maenas), which are comm<strong>on</strong> (introduced) marshpredators in San Francisco Bay (Cohen et al. 1995). Intactuninvaded tidal flat sediment and associated fauna weretransplanted to hybrid Spartina habitat as in <str<strong>on</strong>g>the</str<strong>on</strong>g> transplantexperiment. However, this time we enclosed <strong>on</strong>e individualC. maenas (carapace width 40 mm) in each <str<strong>on</strong>g>of</str<strong>on</strong>g> eightreplicated enclosures (0.3 x 0.3 m x 0.5 m height) made <str<strong>on</strong>g>of</str<strong>on</strong>g>galvanized hardware cloth (0.63-cm mesh). Crabs were- 142 -