Dissertations / Theses on the topic 'Estuary'
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Mitchell, John Dickerson. "Estuary Water Movement." W&M ScholarWorks, 1986. https://scholarworks.wm.edu/etd/1539617567.
Full textTattersall, Graham Richard. "Tamar estuary sediment dynamics." Thesis, Bangor University, 2000. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.341218.
Full textVromans, Deborah Claire. "Macrophyte phenology in a temporarily open/closed Estuary compared with a permanently open Estuary." Thesis, Nelson Mandela Metropolitan University, 2010. http://hdl.handle.net/10948/1393.
Full textLouw, Liezel. "The zooplankton of Mngazana estuary." Thesis, Nelson Mandela Metropolitan University, 2007. http://hdl.handle.net/10948/702.
Full textPritchard, William James. "Anammox in a temperate estuary." Thesis, Queen Mary, University of London, 2014. http://qmro.qmul.ac.uk/xmlui/handle/123456789/8852.
Full textMonteiro, Marcela Cunha. "Natural and anthropogenic control of water quality of an Amazon estuary : the Caeté estuary (Brazil)." Doctoral thesis, Universitat Politècnica de Catalunya, 2017. http://hdl.handle.net/10803/406005.
Full textLos impactos más frecuentes en los estuarios se deben a los asentamientos urbanos no planificados. Como consecuencia de dichos asentamientos, los estuarios se han visto expuestos a una serie de perturbaciones ambientales, tales como el incremento en la entrada de nutrientes y cambios en los usos del suelo y en la hidrología local. En el estuario del río Caeté, objeto de este estudio, las perturbaciones antrópicas originadas en las comunidades de alrededor del estuario y el funcionamiento natural del sistema controlan el input de nutrientes en el estuario. El objetivo principal de esta tesis es analizar la calidad del agua del estuario del río Caeté y la influencia de las forzantes naturales y antrópicas que actúan en él. Para tal efecto, los aspectos climáticos, hidrodinámicos e hidrológicos fueron monitorizados y se identificaron las fuentes potenciales de polución en el estuario. Además, se describieron una serie de potenciales futuros escenarios para el estuario basándose en los procesos naturales y antrópicos que pueden afectar la calidad del agua en las próximas décadas. Los resultados muestran que el input de nutrientes disueltos es mayor en el sector superior del estuario, que concentra el 90% de la población local y tiene una alta incidencia de actividades comerciales (mercados públicos, fábricas de hielo, astilleros, entre otros). Como consecuencia, se observaron aguas eutróficas con altas concentraciones de coliformes fecales (até 1100 NMP/100 ml) durante las mareas vivas en la estación seca, cuando el transporte y/o dilución son menos efectivas. La eutrofización, aunque menos pronunciada, también ocurrió en el resto de sectores (medio y bajo estuario). Sin embargo, estos resultados parecen indicar que esto puede deberse a una condición natural de la región amazónica, la cual es naturalmente enriquecida con una elevada cantidad de nutrientes. Durante mareas muertas, la eutrofización fue menos pronunciada y la calidad de agua presentó mejores condiciones en todas las estaciones monitorizadas. El análisis comparativo ha mostrado que bajo condiciones similares (marea llenante) el estado trófico entre mareas vivar y muertas presenta similitudes. Considerando que la población se incrementa entre 10 y 20% por década en la región, esto puede resultar en un incremento significante de la presión humana y del impacto alrededor del estuario. En este caso, el estado eutrófico observado actualmente podría afectar el estuario de manera permanente. La situación podría agravarse durante la estación seca o eventos de sequía, cuando el estuario es más susceptible a retener los nutrientes. Con el objetivo de mejorar la calidad del agua, se podrían implementar ciertas medidas en el estuario del Caeté basadas en (i) planeamiento urbanístico para controlar la descarga de efluentes en el estuario (ii) construcción de una estación de tratamiento de agua para reducir la entrada de efluentes no tratados y (iii) regular los usos del agua del estuario en función de la calidad de agua.
Ibrahim, Zelina Zaiton. "An integrated approach to the investigation of an equatorial estuary : the Klang River Estuary, Malaysia." Thesis, University of Southampton, 1988. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.328682.
Full textMoore, Rowena Deborah. "Hydrodynamic and Morphometric Modelling of a Macro-Tidal Estuary : The Dee Estuary of NW England." Thesis, University of Liverpool, 2009. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.511030.
Full textKoroknay, Brittani J. "Quantifying Watershed Loads to a Low Relief, Coastal Plain Estuary, the New River Estuary, N.C." W&M ScholarWorks, 2012. https://scholarworks.wm.edu/etd/1539617915.
Full textChan, Terence. "Phytoplankton dynamics in a seasonal estuary." University of Western Australia. Centre for Water Research, 2006. http://theses.library.uwa.edu.au/adt-WU2006.0089.
Full textReeve, Glen M. D. "Sedimentation And Hydrodynamics of Whitianga Estuary." The University of Waikato, 2008. http://hdl.handle.net/10289/2344.
Full textBeckett, C. L. "Heavy metals in Severn Estuary ecosystems." Thesis, University of Bristol, 1986. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.373733.
Full textБондаренко, Юлія Станіславівна, Юлия Станиславовна Бондаренко, Yuliia Stanislavivna Bondarenko, and Ю. С. Коваленко. "Estuary - як останній стандарт англійської вимови." Thesis, Вид-во СумДУ, 2010. http://essuir.sumdu.edu.ua/handle/123456789/16418.
Full textRamirez, Mendoza Rafael. "Flocculation controls in a hypertidal estuary." Thesis, University of Liverpool, 2015. http://livrepository.liverpool.ac.uk/2010209/.
Full textMahamod, Yusuff. "Sedimentary processes in the Dwyryd Estuary." Thesis, Bangor University, 1989. https://research.bangor.ac.uk/portal/en/theses/sedimentary-processes-in-the-dwyryd-estuary(ca0aea23-480c-4032-ba10-12a9adee740c).html.
Full textRodrigues, Ann Maria de Jesus. "Environmental status of a multiple use estuary, through the analysis of bethnic communities : the Sado estuary, Portugal." Thesis, University of Stirling, 1992. http://hdl.handle.net/1893/2597.
Full textBoonphakdee, Thanomsak. "Sources of organic matter and its transportation processes in a tropical river-estuary : the Bangpakong estuary, Thailand." Kyoto University, 2007. http://hdl.handle.net/2433/136568.
Full text0048
新制・課程博士
博士(農学)
甲第13401号
農博第1656号
新制||農||948(附属図書館)
学位論文||H19||N4297(農学部図書室)
UT51-2007-Q802
京都大学大学院農学研究科応用生物科学専攻
(主査)教授 藤原 建紀, 教授 山下 洋, 教授 縄田 栄治
学位規則第4条第1項該当
Chick, Christopher Roberts. "Benthic oxygen production in the choptank estuary." College Park, Md. : University of Maryland, 2009. http://hdl.handle.net/1903/10017.
Full textThesis research directed by: Marine, Estuarine, Environmental Sciences Graduate Program. Title from t.p. of PDF. Includes bibliographical references. Published by UMI Dissertation Services, Ann Arbor, Mich. Also available in paper.
Jianping, Lin. "Iodine speciation in the Yarra River estuary /." Connect to thesis, 1992. http://eprints.unimelb.edu.au/archive/00000216.
Full textWojda, Mark. "Bank Erosion in the Petitcodiac River Estuary." Thesis, Fredericton: University of New Brunswick, 2011. http://hdl.handle.net/1882/35384.
Full textMaier, Gerald. "Nutrients and eutrophication in the Taw estuary." Thesis, University of Plymouth, 2009. http://hdl.handle.net/10026.1/2369.
Full textHerman, W. M. "Wave dynamics in a macro-tidal estuary." Thesis, University of Cambridge, 2000. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.603976.
Full textHoban, T. J. "Polycyclic aromatic hydrocarbons in the Severn Estuary." Thesis, University of South Wales, 1985. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.305737.
Full textCaeiro, Sandra Sofia Ferreira da Silva. "Environmental data management in the Sado Estuary." Doctoral thesis, FCT - UNL, 2004. http://hdl.handle.net/10362/1117.
Full textHodder, Janet. "Production biology of an estuarine population of the green algae, Ulva spp. in Coos Bay, Oregon." Thesis, University of Oregon, 1986. http://hdl.handle.net/1794/9425.
Full textElston, Susan Anne. "Secondary Circulation in a Sinuous Coastal Plain Estuary." Diss., Available online, Georgia Institute of Technology, 2005, 2005. http://etd.gatech.edu/theses/available/etd-05042005-143327/.
Full textDr. Curry, Judith, Committee Co-Chair ; Dr. Blanton, Jackson - Committee Chair, Committee Chair ; Dr. Cunnold, Derek, Committee Member ; Dr. Seim, Harvey, Committee Member ; Dr. Webster, Donald, Committee Member ; Dr. Webster, Peter, Committee Member ; Dr. Wong, Kuo, Committee Member.
Deyzel, (Shaun) Herklaas Phillipus. "Mesozooplankton dynamics in a biogeographical transition zone estuary." Thesis, Nelson Mandela Metropolitan University, 2012. http://hdl.handle.net/10948/d1007901.
Full textBourgault, Daniel. "Circulation and mixing in the St. Lawrence estuary." Thesis, McGill University, 2001. http://digitool.Library.McGill.CA:80/R/?func=dbin-jump-full&object_id=37871.
Full textThe seasonal variability of the general circulation and mixing is examined with a newly developed laterally averaged numerical model. The model takes into account tidal forcing and a realistic topography while forced with a large seasonal change in the river discharge. The model is able to reproduce important processes associated with the tidal forcing and mean conditions (density field, residual circulation). The numerical results show that mixing in the St. Lawrence Estuary is not evenly distributed. Mixing is found to be large near the sill at the head of the Laurentian Channel, as previously thought, as well our new results show that equivalent levels of mixing are also found near English Bank and near Ile-aux-Coudres. During the spring freshet, when the river discharge is 40% higher than normal, the limit of salt intrusion is moved seaward by approximately 12 km, the residual circulation is intensified by approximately 10%, and the turbulent vertical mass flux increases throughout owing to greater availability of freshwater. The results also suggest that during high runoff periods, the vertical stability of the water column increases in the upper estuary.
The model is also used to assess the impacts of climate change on the estuarine dynamics. (Abstract shortened by UMI.)
Gow, T. A. K. "Studies on benthic microalgae in a polluted estuary." Thesis, University of the West of Scotland, 1985. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.354365.
Full textNairn, H. J. "Fish fauna of the Avon-Heathcote Estuary, Christchurch." Thesis, University of Canterbury. Zoology, 1998. http://hdl.handle.net/10092/6872.
Full textFindlay, John Smith. "Geochemistry of suspended particles in the Tamar estuary." Thesis, University of Plymouth, 1990. http://hdl.handle.net/10026.1/514.
Full textUpstill-Goddard, R. C. "Geochemistry of the halogens in the Tamar estuary." Thesis, University of Leeds, 1985. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.354529.
Full textWANDERLEY, CRISTIANA VILLELA DE ARAUJO. "SEDIMENTATION RATES CHANGES AT PARAÍBA DO SUL ESTUARY." PONTIFÍCIA UNIVERSIDADE CATÓLICA DO RIO DE JANEIRO, 2013. http://www.maxwell.vrac.puc-rio.br/Busca_etds.php?strSecao=resultado&nrSeq=24946@1.
Full textCOORDENAÇÃO DE APERFEIÇOAMENTO DO PESSOAL DE ENSINO SUPERIOR
PROGRAMA DE SUPORTE À PÓS-GRADUAÇÃO DE INSTS. DE ENSINO
A cidade de Atafona situada à foz do Rio Paraíba do Sul (RPS) vem sofrendo erosão em sua linha de costa por muitas décadas. Este estudo consiste em uma avaliação das taxas de sedimentação no estuário do Paraíba do Sul e suas correlações com a forte erosão que ocorre em Atafona, Rio de Janeiro. O trabalho foi baseado em quatro transetes ao longo do Estuário do rio Paraíba do Sul contendo 14 pontos de coleta. Cerca de 540 amostras de sedimentos foram obtidas em Janeiro de 2010 e Fevereiro de 2011. As taxas de sedimentação foram determinadas a partir do método da datação com 210Pb e os inventários de 210Pb foram determinados para todos os pontos de coleta. Foram aplicados dois modelos para a determinação das taxas de sedimentação: o modelo da Concentração Inicial Constante (modelo CIC) e o modelo da Razão de Suprimento Constante (modelo CRS). Os resultados da datação 210Pb foram validados com base na variação da concentração elementar ao longo de dois testemunhos. A determinação de elementos foi realizada utilizando a técnica de Espectrometria de Massa com Plasma Indutivamente Acoplado (ICP-MS). A análise multivariada de dados foi aplicada através da análise de fatores principais (AFP) e análise hierárquica de cluster (AHC) a fim de obter informações que traduzam quantitativamente a composição dos sedimentos descrevendo a região. Os inventários de 210Pb determinados nos pontos de coleta, localizados ao sul do rio Paraíba do Sul (RPS), foram maiores do que os determinados nos pontos de coleta localizados ao centro e ao norte da saída do rio. O valor médio do inventário obtido nos pontos de coleta ao sul da foz do RPS foi de 1,0 Bq cm-2, muito superior ao valor médio obtido nos pontos situados ao norte da foz do rio, com valor de 0,16 Bq cm-2, indicando que os sedimentos são transportados na direção sul da foz do RPS, ao longo da costa com as correntes de deriva existentes nesta direção. A taxa de acumulação estimada para as camadas mais profundas foi de 0,06 g cm-2 ano-1. Essa taxa representa um valor base para a taxa de acumulação de sedimentos para o período anterior a 1950. As taxas de acumulação obtidas para o período mais recente variaram de 0,2 g cm-2 ano-1 nos pontos situados ao norte e ao centro a 0,6 g cm-2 ano-1 nos pontos situados ao sul da foz do RPS. Observou-se que as concentrações de Cr, Cu, Cd e Zn aumentaram significativamente a partir dos anos oitenta que, coincide com a época do acidente ocorrido com a Cia. de Paraibuna Metais em 1982. Uma das consequências nas mudanças no uso da terra e do represamento de rios é a mudança na natureza dos sedimentos que chegam e se depositam no delta do RPS. A normalização da concentração dos metais pelo alumínio pode ajudar a traçar tais mudanças, principalmente com elementos de origem distinta, como Ca e Mg. Através da curva obtida entre razão a Mg/Al e as idades das camadas sedimentares pode-se observar uma forte mudança no período entre 1962 e 1988. Foram identificados quatro fatores através da AFP traduzindo quatro fases do sedimento: duas representando a matriz, uma representando os carbonatos e a outra representando os sulfetos.
The city of Atafona, situated at Paraíba do Sul Estuary, has been suffering erosion in its coastline for decades. This study is an evaluation of sedimentation rates in the Paraíba do Sul estuary and its correlation with the strong erosion that occurs in Atafona city, Rio de Janeiro, Brazil. We performed four transects along Paraíba do Sul Estuary with 14 sampling points. About 540 sediment samples were collected in January 2010 and February 2011. Sedimentation rates were determined by 210Pb dating method and inventories of 210Pb were determined for all sampling points. Two models were applied for the sedimentation rates determination: the Constant Initial Concentration model (CIC-model) and the Constant Rate of Supply model (CRS-model). The 210Pb dating results were validated based on the elemental concentration variation throughout two of the sediment cores. The elements determination was performed using the mass spectrometry with inductively coupled plasma technique (ICP-MS). The multivariate analysis were applied trough the principal factor analysis (PFA) and hierarchical cluster analysis (HAC) in order to obtain factors that may traduce quantitatively the sample composition describing the region. At sampling points located at south of the Paraiba do Sul River (PSR) mouth, 210Pb inventories were higher than those at the northern and central sampling locations. The inventory average obtained at south was 1.0 Bq cm-2, much higher than those located at north of the river mouth, with a mean value 0.16 Bq cm-2, indicating that the sediments are transported southward by the alongshore current. The accumulation rate estimated for the deeper layers was 0.06 g cm-2 yr-1, which represents a reference value of sediment accumulation rate for the period prior to 1950. Accumulation rates obtained for the most recent period ranged from 0.2 g cm-2 yr-1 in the points situated at north and center to 0.6 g cm-2 yr-1 in points located at south of RPS mouth. It was observed that Cr, Cu, Cd and Zn concentrations increased significantly from the eighties that matches with the Cia Paraibuna Metals accident occurred in 1982. A consequence of changes in land use and the damming of the river is a change in the nature of the particulates reaching the PSR delta. The normalization of elemental concentrations to aluminum could help trace these changes, particularly for elements with a distinct origin, such as Ca and Mg. The Mg/Al versus ages plot showed a strong change between 1962 and 1988. There were four factors identified that traduce four sediment phases, two of them were related to the matrix, other was related to the carbonate phase and the other representing sulfides phase.
Woodruff, Jonathan Dalrymple. "Sediment deposition in the lower Hudson River estuary." Thesis, Massachusetts Institute of Technology, 1999. http://hdl.handle.net/1721.1/80032.
Full textIncludes bibliographical references (leaves 54-57).
by Jonathan Dalrymple Woodruff.
S.M.in Civil and Environmental Engineering
Hegermiller, Christie A. "Fine Sediment Trapping in the Penobscot River Estuary." Thesis, Boston College, 2011. http://hdl.handle.net/2345/2000.
Full textThe Penobscot River Estuary is heavily contaminated with mercury; previous studies indicate maximum mercury concentrations of 4.6 ppm within the Frankfort Flats reach. The transport and trapping of this contaminant is linked to the transport and trapping of fine sediment within the estuary. Hydrographic and flow measurements, coupled with a spatial and temporal characterization of the bottom sediments, were performed during and following the freshet in 2010 to determine the mechanisms driving sediment transport and trapping within the estuary. The Penobscot River likely has a turbidity maximum associated with the landward extent of the salinity intrusion that is positioned over the Frankfort Flats reach during average discharge and tidal conditions. This turbidity maximum may be responsible for a patch of fine sediments in the Frankfort Flats reach in an otherwise coarse-grained bed. Additional transport and trapping of fine sediments within this reach is the result of secondary circulation driven by centripetal acceleration around meanders in the channel. Close proximity of meanders at Frankfort Flats, within ~5 km, creates opposite secondary circulation of magnitude ~0.2 m/s during flood and ebb conditions
Thesis (BS) — Boston College, 2011
Submitted to: Boston College. College of Arts and Sciences
Discipline: Geology & Geophysics Honors Program
Discipline: Earth and Environmental Sciences
Amini, Sina. "Hydrodynamics and Salinity of Pontchartrain Estuary During Hurricanes." ScholarWorks@UNO, 2014. http://scholarworks.uno.edu/td/1845.
Full textWatts, Sarah Jane. "Recovery of the Mersey Estuary from metal contamination." Thesis, University of Plymouth, 2004. http://hdl.handle.net/10026.1/2133.
Full textAbdulkade, Akirat. "The dynamics of Cobble Dunes, Severn Estuary UK." Thesis, University of Southampton, 2017. https://eprints.soton.ac.uk/415839/.
Full textViskich, Michal. "Long-term changes in a small, urban estuary." Bachelor's thesis, University of Cape Town, 2014. http://hdl.handle.net/11427/12825.
Full textThe Diep River estuary is a small, urban estuary situated in the suburbs of Cape Town and has been subjected to long-term modifications and abuse that far exceeds that of most other estuaries around South Africa. Activities in the Diep River catchment, together with the intensive urban development in the areas adjacent to the estuary, have resulted in massive changes in biodiversity, altered flow and salinity regimes; causing a marked deterioration in water quality and a frightening increase in non-indigenous species introductions. Several studies have been undertaken at the Diep River estuary, however, they are out-dated and many changes have occurred within the last few decades. The aim of this study was to provide an up-to-date list of the fauna residing within the Diep River estuary, as well as to provide a synthesis of all the major physical, hydrological and faunistic changes that have occurred within and around the estuary, dating back to the late 1800s, whereas faunistic changes are described using information provided by several earlier surveys dating back to the early 1950s. Infauna, epifauna and salinity were taken at designated stations along Milnerton Lagoon. Prawn (Callichirus kraussi) counts were also made in order to determine current abundance and distribution. Results showed a substantial decline in sand prawn abundance with the estimated standing stock calculated at just over 12 million. Fauna collected were generally poor in abundance and were mainly limited to euryhaline, detritus feeders. Earlier surveys conducted in the 1950s recorded at least 49 infauna and epifauna species residing within Milnerton Lagoon, whereas in 1974, only 23 species were found. Similarly, 24 species were recorded in this study. The European shore hopper (Orchestiagammarella) was recorded as a new introduction within the system. Only five fish species were recorded in the summer period, including the highly invasive mosquito fish (Gambusiaaffinis), which was found in relatively high abundance within the lagoon. A regular monitoring of the infauna and epifauna populations for this system needs to be established, in order to obtain a clear picture of the faunistic distribution and changes occurring within this highly dynamic environment. Additionally, serious management protocols need to be established in order to prevent the further degradation of this important system.
Rosa, Mónica Sofia Soares. "Hydrodynamical and biogeochemical modeling study of Sado estuary." Master's thesis, Universidade de Aveiro, 2010. http://hdl.handle.net/10773/7392.
Full textThe Sado estuary is located in the surrounding area of an important Portuguese natural park (Arrábida Natural Park) near the city of Setúbal. The low freshwater discharge from Sado River, the mesotidal tide along the estuary and the strong currents observed turn the estuary a well‐mixed system, controlling the estuarine residence time, and therefore determining the patterns of conservative and nonconservative tracers. The salt dynamics inside this kind of system is very important, since salinity may be considered a natural tracer, allowing the comprehension of the dynamics of other conservative tracers. In such a system is also important to analyze the water quality determining the coliforms propagation from selected discharge stations and analyzing its relation with the estuarine hydrographic features. In this study, a two‐dimensional hydrodynamic model is implemented for the Sado estuary in order to study the horizontal patterns of salinity, as well as the propagation of fecal coliforms from sewage stations, both under different tidal and freshwater forcing conditions. The model used in this study is Mohid‐2D (www.mohid.com), a marine model that uses the shallow water approximation to study vertically homogeneous systems like the Sado estuary. The model domain includes the whole area of the estuary, using a realistic coastline and bottom topography The model results are explored in order to evaluate salinity differences between flood and ebb, spring and neap tide, and low (2m3s‐1), medium (50m3s‐1) and high (200m3s‐1) river inflow. Moreover, the propagation of fecal coliforms from sewage stations is also studied in light of different tidal and freshwater inflow conditions. Sea surface height and velocity model outputs are compared to in‐situ data, revealing the model skill in reproducing the tidal propagation along the Sado estuary. When the river inflow is weak (2m³/s), the hydrography of the estuary is clearly tidal dominated but when the river inflow is high (200m³/s), the horizontal patterns of salinity inside the estuary are determined by a balance between tide and river inflow effects. In this case is found a classic division of the estuary in three distinct regions: marine, mixing and freshwater. In this last region the estuary dynamics is mainly modulated by the freshwater discharge. Despite the significant estuarine dynamics, the concentration of fecal coliforms was found confined to small areas close to the discharge points. These organisms were found to affect only a restricted area near the sewage stations, with low concentrations found far the discharge points along the estuary.
O estuário do Sado encontra‐se inserido no parque natural da Arrábida junto à cidade de Setúbal. A baixa descarga de água doce proveniente do rio Sado, a maré mesotidal ao longo do estuário e as fortes correntes que aqui se observam tornam o estuário um sistema bem misturado, controlando o tempo de residência e determinando assim os padrões de traçadores conservativos e não conservativos. A dinâmica salina no interior deste tipo de sistemas é muito importante, uma vez que a salinidade pode ser considerada um traçador natural, permitindo a compreensão da dinâmica de outros traçadores. Num sistema como este, é também importante analisar a qualidade da água, determinando a propagação de coliformes provenientes de estações de descargas seleccionadas e analisando a sua relação com as estruturas hidrográficas do estuário. Neste estudo, um modelo hidrodinâmico bidimensional é implementado para o estuário do Sado, com o objectivo de estudar os padrões horizontais de salinidade, bem como a propagação de coliformes fecais com origem em estações de esgoto locais. São avaliadas condições distintas de maré (maré‐viva, maré‐morta), diferentes fases da mesma (enchente e vazante) e descargas características do caudal fluvial (baixo (2m3s‐1), médio (50m3s‐1) e elevado (200m3s‐1)). O modelo usado neste estudo foi o MOHID‐2D (www.mohid.com), um modelo marinho que utiliza a aproximação de águas pouco profundas para estudar sistemas verticalmente homogéneos, como é o caso do estuário do Sado. O domínio do modelo abrange toda a área do estuário, usando a linha de costa e topografia de fundo realista. Os resultados do modelo são explorados de modo a avaliar as diferenças de salinidade entre enchente e vazante, maré‐viva e maré‐morta e baixo, médio e elevado caudal fluvial. Posteriormente foi ainda estudada a propagação de coliformes fecais nas condições anteriormente referidas. As previsões do modelo em termos de velocidade e nível de maré são comparadas com observações in situ, revelando a capacidade do modelo em reproduzir adequadamente a propagação de maré ao longo do estuário do Sado. Quando o caudal fluvial é fraco (2m3s‐1), a hidrografia do estuário é claramente dominada pela maré, quando este é elevado (200m3s‐1) os parâmetros horizontais de salinidade dentro do estuário são determinados por um balanço entre o efeito da maré e do caudal fluvial. Neste caso é perceptível a divisão do estuário em três regiões: marinha, de mistura e de água doce. Nesta última a dinâmica do estuário é principalmente modulada pela descarga de água doce proveniente do rio. Apesar da dinâmica estuarina, as concentrações de coliformes fecais mostraram estar confinadas a pequenas áreas junto às estações de descarga de esgoto, sendo detectadas concentrações bastante baixas em zonas mais afastadas dos pontos de descarga e ao longo do estuário.
Arnott, Kimberly. "Friction-dominated water exchange in a Florida estuary." [Gainesville, Fla.] : University of Florida, 2009. http://purl.fcla.edu/fcla/etd/UFE0041345.
Full textPearson, Holly Beverley Clare. "Copper and zinc speciation in the Tamar Estuary." Thesis, University of Plymouth, 2017. http://hdl.handle.net/10026.1/9584.
Full textBoyer, Joseph N. "Degradation and mineralization of chitin in an estuary." W&M ScholarWorks, 1987. https://scholarworks.wm.edu/etd/1539616579.
Full textTaylor, Arthur. "A trace element study of sediments from the Olifants River estuary, the Berg River estuary, and the off-shore Mud Belt." Master's thesis, University of Cape Town, 2004. http://hdl.handle.net/11427/9027.
Full textTrace elements have received increased attention since the mid-1900's. Although some studies have investigated trace element accumulation as a result of urban expansion in the Western Cape, South Africa, few have catalogued the accumulation and behavior of trace elements resulting from agricultural practices. This study investigates the distribution and behavior of trace elements for the Olifants and Berg river catchments by focusing on the sediments of the estuaries. The dominant industry in both catchments is agriculture and there exists relatively little urban sprawl. Two sediment samples taken from the offshore mud belt in the vicinity of the two river mouths were also analyzed. The sediments were analyzed for trace elements using inductively coupled plasma mass spectrometry (ICP-MS), major elements using X-ray fluorescent spectroscopy (XRF), total sulfur using XRF, total and organic carbon using a C:H:N analyzer, and grain size analysis was performed (>62 μm, 38-63 μm, 2-38 μm, <2μm). The mud belt cores were dated using 14C dating. Estuarine surface waters were analyzed for trace elements, pH, dissolved oxygen (DO), electrical conductivity (EC), and temperature. The trace elements arsenic (As), cadmium (Cd), copper (Cu), lead (Pb), and zinc (Zn) were focused on. The trace element concentrations in the sediments were compared with those of soils that occur in the study area, as well as their parent materials, to determine background concentrations. The concentration profiles of elements with respect to depth are compared with natural deposition rates to recognize signs of recent enrichment of individual trace elements. Inter-element comparisons are made in an attempt to determine speciation. Comparison between the estuarine and mud belt sediments were made to assess the estuaries ability to filter fluvial trace elements, as well as to determine the sediment contributions of the Olifants and Berg rivers to the mud belt. Statistical analysis was performed to"group sediment populations Trace element and organic matter concentrations showed strong positive correlations with fine-sized particles. The mud belt sediments displayed considerably more OC than the estuarine sediments. The trace elements appear to associate predominantly with clay minerals (alumino-silicates), Fe/Mn oxides, and organic matter. Trace element correlations with S and carbonate carbon were also observed. Comparison with estimates of natural deposition rates and compositions of soils occurring in the catchments did not suggest an anthropogenic pollution input. From the data available the estuarine and Mud Belt sediments appear enriched in Cd, Cu and Zn in comparison to the background soils. The estuaries seem to effectively trap Zn and Pb, but do not capture As well. Statistical analysis suggest that, of the rock types considered, the sediments of the Olifants and Berg river estuaries and those of the off shore mud belt are most similar to sediments derived from the Malmesbury and Ecca Groups. The Olifants and Berg rivers are important sources of water for the farming community, as well as for municipal use in the Western Cape. Based on this investigation of the estuarine waters and sediments the rivers appear to be in good health in regards to trace element concentrations.
Groenewald, Christoff J. "Macrobenthic community structure across an inter- and subtidal gradient in a mangrove estuary." Thesis, Nelson Mandela Metropolitan University, 2010. http://hdl.handle.net/10948/1240.
Full textFernandes, Elisa Helena. "Modelling the hydrodynamics of the Patos Lagoon, Brazil." Thesis, University of Plymouth, 2001. http://hdl.handle.net/10026.1/679.
Full textDaka, Erema Ransome. "Population differences in the toxic effects of heavy metals to Littorina saxatilis olivi (prosobranchia: Mollusca)." Thesis, University of Liverpool, 1996. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.320573.
Full textMcKelvey, Fionnuala. "Population ecology and fisheries management of the native oyster, Ostrea edulis L. in Lough Foyle." Thesis, University of Ulster, 1996. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.241729.
Full textGeorge, Christian Robert. "Variation in the erosion threshold of natural intertidal sediments." Thesis, University of Bristol, 1994. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.261239.
Full textJulyan, Enrique Edward. "Interrelationship of the fluvial morphology and the salinity of the Great Fish River Estuary." Thesis, Stellenbosch : Stellenbosch University, 2015. http://hdl.handle.net/10019.1/96952.
Full textENGLISH ABSTRACT: The investigation of the interrelationship of the fluvial morphology and the salinity of the Great Fish River Estuary was performed by the combination of a two-dimensional morphological model and a one dimensional advection dispersion module. Two scenarios were defined for investigation, namely Scenarios A and B. Model bathymetry and grid/network for each model and scenario was compiled from topographical information obtained from aerial photos, SRTM data, LIDAR and 24 measured river cross sections of the area from the river mouth up to 27km upstream of the river mouth. Model boundary conditions were developed from empirical formulas and measured data from the Department of Water and Sanitation (DWS). Both models were calibrated with results obtained during field measurement conducted from 5 – 7 May 2012. Scenario A consisted of a long term 5 year morphological simulation (1 May 2007 to 30 May 2012) with manual mouth closure events for identified river low flow periods. Water levels upstream of the river mouth were extracted from the two-dimensional morphological module and used as the downstream boundary condition of the one-dimensional advection dispersion (salinity) model. For scenario B floods with return periods between 1:2 and 1:100 years were simulated in the morphological model. The resultant bathymetries were then used to compile the network and bathymetry of the one dimensional advection dispersion (salinity) model. The different flood resultant bathymetries were then used with equal boundary conditions (representative of the average flow in the river) in the one dimensional salinity model. The predicted salinity was compared for each bathymetry used. From model results distinct trends were observed. During low flow conditions the estuary basin fills with sediments and during floods the sediments are flushed out of the estuary. Large magnitude floods greatly erode the estuary especially in the middle reach, during floods the tidal inlet experiences overtopping and subsequent erosion, the constriction at the tidal inlet is completely destroyed during larger floods. The estuary mouth in its closed state experiences slight overtopping and the mouth is breached during periods of high river flows. The magnitude of salt intrusion depends mainly on the size (the constriction) of the river mouth (tidal inlet). During periods of mouth closure the average salinity in the estuary decreases, average salinity increases if the tidal inlet area is increased. The extent of salt intrusion is approximately 10 km upstream of the river mouth when the mouth is open and the intrusion length increases during spring tides.
AFRIKAANSE OPSOMMING: Die verwantskap tussen die Groot Vis Rivier Estuarium morfologie en sout toestand is ondersoek deur die kombinasie van ‘n twee dimensionele morfologiese model en ‘n een dimensionele sout model. Twee toestande is gedefinieer vir ondersoek naamlik Scenario A en Scenario B. Die area vanaf die rivier mond tot 27 km stroomop van die rivier mond is deur die modelle gesimuleer. Die gemodeleerde area stem ooreen met die area waar gemete rivier-snit diepte metings beskikbaar was, onbrekende data is aangevul met behulp van lugfotos, LIDAR- en SRTM- data. Die model grens toestande is bepaal met empiriese vereglykings asook gemete data vanaf die Departement Waterwese. Beide numeriese modelle was gekalibreer met veld data verkry vanaf 5 tot 7 Mei 2012. Scenario A het behels ‘n langtermyn 5 jaar morfologiese modellering (1 Mei 2007 tot 30 Mei 2012) met toemond toestande gedurende gedefinieerde rivier vloei toestande. Die watervlakke van die twee dimensionele morfologiese model stroomop van die mond is gebruik as die stroomaf grenstoestand van die een dimnesionele model om die effek van die morfologiese veranderinge te inkorporeer in die sout model. Scenario B het behels die simulering van rivier vloede met herhaal periodes tussen 1:2 en 1:100 jaar in die morfologiese model. Die rivier-bodem vlakke verkry van laasgenoemde simulasiesis toe gebruik in die een dimensionele sout model met dieselfde grenstoestande wat ooreenstem met die gemiddelde toestande in die Groot Vis Rivier. Aangesien die grenstoestande dieselfde was en net die rivier-bodem vlakke gevarieer is, kon die effek van vloede op die souttoestand in die estuarium bepaal word. Uit die model resultate kon duidelike tendense waargeneem word. Gedurende lae rivier vloei toestande is die estuarium gevul met sediment en tydens vloede het die sediment weer ge-erodeer en gedeponeer in die oseaan. Groot vloede veroorsaak baie erosie in die estuarium veral in die middel bereik en by die riviermonding. Indien die vloed groot genoeg is word die riviermond vernouing totaal uitgespoel. Die riviermonding in die geslote staat ondervind effense oorstroming en word oopgespoel indien die rivier vloei groot genoeg is. Die graad van die sout indringing in die estuarium hang hoofsaaklik af van die grootte (die vernouing) van die rivier mond. Gedurende toe mond toestande is die gemiddelde sout vlakke in die estuarium laer, wanner die rivier monding groter raak, word die gemiddelde sout vlakke in die estuarium meer. Die omvang van die sout indringing strek tot ongeveer 10 km stroomop van die rivier mond wanneer die mond oop is en die indringing afstand neem toe gedurende spring getye.