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Dinámica del arsénico (As), cadmio (Cd), plomo (Pb), ZINC (Zn) Y mercurio (Hg) humedales de la confluencia de los ríos Cauca y Magdalena, Colombia

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dc.audience
dc.contributor.advisorMarrugo Negrete, José Luisspa
dc.contributor.authorBravo Ferro, Eva Melisa
dc.date.accessioned2023-08-28T13:05:19Z
dc.date.available2025-08-08
dc.date.available2023-08-28T13:05:19Z
dc.date.issued2023-04-28
dc.description.abstractEn este estudio se determinaron las concentraciones de cinco elementos potencialmente tóxicos (EPTs) mercurio (Hg-T), plomo (Pb), cadmio (Cd), arsénico total (As-T) y zinc (Zn) en ocho ciénagas de la confluencia de los ríos Cauca y magdalena, su distribución en seis especies de macrófitas (Eichornia crassipes, Neptunia oleracea, Polygonum densiflorum, Paspalum repens, Eichornia azurea y Ludwigia helminthorrhiza) y su concentración en agua y sedimentos, así como también el FBC y FT en las diferentes especies. Las concentraciones de EPTs se trataron de acuerdo con el método EPA 200.2 (USEPA 2007) el caso del agua y se analizaron mediante espectrometría de absorción atómica (APHA 1998). En lo que respecta a los sedimentos fueron procesados siguiendo el método 3051 A (USEPA, 2007) y las macrófitas a través del método EPA 200.3 (USEPA 1991a). Los resultados mostraron una mayor concentración de Zn en agua, sedimentos y macrófitas, la tendencia en concentración siguió el orden decreciente Zn>Cd>As>Pb>Hg en las especies y Zn>Pb>As>Hg>Cd tanto en agua como en sedimentos. La ciénaga la Redonda fue la que registro valores máximos de este elemento (377.45 μg/g sedimento y 211.5 μg/L agua) entre tanto que la especie Ludwigia helminthorrhiza mostro una concentración máxima de 321.83μg/g. Hubo fuertes correlaciones significativas (p < 0.05) entre los EPTs en sedimentos y agua, pero escasas entre estos compartimentos y las especies. En cuanto al FBC y FT en la mayoría de las especies se establecieron resultados análogos entre estos factores solo la especie Neptunia oleracea obtuvo valores de FBC> 1 y TF > 1 para Cd otorgándole la capacidad de fitoextractora.spa
dc.description.degreelevelMaestríaspa
dc.description.degreenameMagíster en Ciencias Ambientalesspa
dc.description.modalityTrabajos de Investigación y/o Extensiónspa
dc.description.tableofcontents1. INTRODUCCIÓN ........................................................................................ 8spa
dc.description.tableofcontents2. MARCO DE REFERENCIA ................................................................... 10spa
dc.description.tableofcontents2.1 ANTECEDENTES ................................................................ 10spa
dc.description.tableofcontents2.2 MARCO TEÓRICO ................................................ 12spa
dc.description.tableofcontents2.2.1 Elementos potencialmente tóxicos (EPTs) ............................................12spa
dc.description.tableofcontents2.2.2. Elementos esenciales y no esenciales .............................................13spa
dc.description.tableofcontents2.2.3 Contaminación de ecosistemas acuáticos continentales por metales pesados ................................................................................. 16spa
dc.description.tableofcontents2.2.4. Contaminación con elementos potencialmente tóxicos e impactos sobre la biota y ecosistemas de humedales .............................18spa
dc.description.tableofcontents2.2.5 Macrófitas........................................................................................... 20spa
dc.description.tableofcontents2.2.6 Descripciones de las Especies de Macrófitas ................................... 20spa
dc.description.tableofcontents2.2.7. Dinámica de los elementos potencialmente tóxicos en plantas acuáticas............................................................................................... 25spa
dc.description.tableofcontents2.2.8. Factores de Bioconcentración y Traslocación ................................... 26spa
dc.description.tableofcontents3. OBJETIVOS ...................................................................................... 27spa
dc.description.tableofcontents4.1. ÁREA DE ESTUDIO ................................................................. 28spa
dc.description.tableofcontents4.2. Fase de campo.................................................................................... 29spa
dc.description.tableofcontents4.2.1 Colecta de las muestras (macrófitas, agua y sedimentos)............................................................................................30spa
dc.description.tableofcontents4.3. Fase de Laboratorio ................................................................................. 31spa
dc.description.tableofcontents4.4. Control de calidad de los métodos............................................................... 31spa
dc.description.tableofcontents4.5. Análisis de datos ..................................................................................................... 32spa
dc.description.tableofcontents5. RESULTADOS Y DISCUSIÓN ......................................................................... 32spa
dc.description.tableofcontents5.1. Composición y abundancia de plantas vasculares acuáticas en ocho ciénagas de la cuenca del Magdalena .............................................. 32spa
dc.description.tableofcontents5.2. Concentraciones de EPTs en las diferentes especies de macrófitas de ocho ciénagas de la confluencia de los ríos Cauca y Magdalena .............................................................................................................. 35spa
dc.description.tableofcontents5.3. Concentraciones de elementos potencialmente tóxicos en agua de ocho ciénagas del Magdalena, Bolívar .................................................. 39spa
dc.description.tableofcontents5.4. Concentraciones de elementos potencialmente tóxicos en sedimentos de 8 ciénagas del Magdalena, Bolívar .............................. 41spa
dc.description.tableofcontents5.5. Factor de Bioconcentración (BAF) y de Translocación (FT) ............................................................................................................... 42spa
dc.description.tableofcontents5.6. Correlación de las concentraciones de elementos potencialmente tóxicos en agua, sedimentos con especies de macrófitas ..................................................................................................... 48spa
dc.format.mimetypeapplication/pdfspa
dc.identifier.urihttps://repositorio.unicordoba.edu.co/handle/ucordoba/7759
dc.language.isospaspa
dc.publisherUniversidad de Córdoba
dc.publisher.facultyFacultad de Ciencias Básicasspa
dc.publisher.placeMontería, Córdoba, Colombiaspa
dc.publisher.programMaestría en Ciencias Ambientalesspa
dc.rightsCopyright Universidad de Córdoba, 2023spa
dc.rights.accessrightsinfo:eu-repo/semantics/embargoedAccessspa
dc.rights.creativecommonsAtribución-NoComercial-SinDerivadas 4.0 Internacional (CC BY-NC-ND 4.0)spa
dc.rights.urihttps://creativecommons.org/licenses/by-nc-nd/4.0/spa
dc.subject.keywordsEPTsspa
dc.subject.keywordsMacrophytesspa
dc.subject.keywordsSwampsspa
dc.subject.keywordsCauca riverspa
dc.subject.keywordsMagdalena riverspa
dc.subject.proposalEPTsspa
dc.subject.proposalMacrófitasspa
dc.subject.proposalCiénagasspa
dc.subject.proposalRio Caucaspa
dc.subject.proposalRio Magdalenaspa
dc.titleDinámica del arsénico (As), cadmio (Cd), plomo (Pb), ZINC (Zn) Y mercurio (Hg) humedales de la confluencia de los ríos Cauca y Magdalena, Colombiaspa
dc.typeTrabajo de grado - Maestríaspa
dc.type.coarhttp://purl.org/coar/resource_type/c_bdccspa
dc.type.contentTextspa
dc.type.driverinfo:eu-repo/semantics/masterThesisspa
dc.type.versioninfo:eu-repo/semantics/submittedVersionspa
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