Regulation of Estuarine Biogeochemical Processes by Cyanobacterial Blooms

dc.contributor.advisorCornwell, Jeffrey C.en_US
dc.contributor.advisorStoecker, Diane K.en_US
dc.contributor.authorGao, Yonghuien_US
dc.contributor.departmentMarine-Estuarine-Environmental Sciencesen_US
dc.contributor.publisherDigital Repository at the University of Marylanden_US
dc.contributor.publisherUniversity of Maryland (College Park, Md.)en_US
dc.date.accessioned2012-07-10T05:31:02Z
dc.date.available2012-07-10T05:31:02Z
dc.date.issued2011en_US
dc.description.abstractNutrient supply, including `new' nitrogen (N) added through N<sub>2</sub>-fixation, nutrient release from sediments and freshwater inflow, can be important in increasing and sustaining estuarine phytoplankton blooms. In return, dense blooms in shallow water estuaries may affect nutrient recycling by elevating the pH and dissolved oxygen (DO) concentrations as well as increasing sedimentation of phytoplankton detritus. My dissertation addressed the interaction between cyanobacterial blooms and biogeochemical nutrient recycling in the tidal-fresh and oligohaline region of the Sassafras River, a tributary of the Chesapeake Bay, Maryland, USA. When high pH overlying water comes in contact with sediments, the subsequent pH penetration causes desorption of exchangeable ammonium and converts NH<sub>4</sub> <super>+</super> to NH<sub>3</sub> from both porewater and absorbed NH<sub>4</sub> <super>+</super> pools. Alkaline pH and the toxicity of NH<sub>3</sub> may inhibit nitrification in the thin aerobic zone. During massive cyanobacterial blooms in summer, high effluxes of SRP and total ammonium from sediments were associated with reduced nitrification and denitrification rates. Retention of N in the upper estuary and increased dissolved inorganic nitrogen (DIN) release into the water column may facilitate nitrogen assimilation by cyanobacteria in N-limited water. High pH also resulted in a significant increase in soluble reactive phosphate (SRP) flux and lead to relatively high SRP compared to DIN flux rates, which may support the high P demand of diazotrophic cyanobacteria. As N became limiting in summer, the dominant cyanobacterial assemblage changed from non-N<sub>2</sub> fixers (Microcystis spp.) to N2 fixers (<italic>Anabaena </italic> spp., <italic>Pseudanabaena </italic> sp. and <italic>Synechococcus </italic> sp.). Warm temperatures, high P availability and low salinity are environmental factors associated with high rates of N2 fixation. Dissolved inorganic carbon (DIC) limitation, high pH, and high DO concentrations, mediated by cyanobacterial photosynthesis, can cause decreases in photosynthetic efficiency and daytime N<sub>2</sub> fixation of the cyanobacterial assemblage. Species succession appears to enable the cyanobacterial assemblage to adapt to changing environmental conditions caused by the bloom, including high pH and DO, and to maintain N<sub>2</sub> fixation for sustained growth.en_US
dc.identifier.urihttp://hdl.handle.net/1903/12773
dc.subject.pqcontrolledEnvironmental scienceen_US
dc.subject.pqcontrolledBiogeochemistryen_US
dc.subject.pqcontrolledBiological oceanographyen_US
dc.subject.pquncontrolledCoupled nitrification-denitrificationen_US
dc.subject.pquncontrolledCyanobacterial bloomsen_US
dc.subject.pquncontrolledNitrogen fixationen_US
dc.subject.pquncontrollednutrient flux at the sediment-water interfaceen_US
dc.subject.pquncontrolledNutrient inputen_US
dc.subject.pquncontrolledpH and dissolved oxygenen_US
dc.titleRegulation of Estuarine Biogeochemical Processes by Cyanobacterial Bloomsen_US
dc.typeDissertationen_US

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