Publicación: Contaminantes emergentes (productos farmacéuticos y de cuidado personal) en aguas y sedimentos de ecosistemas acuáticos del departamento de Córdoba-Colombia
dc.contributor.advisor | Marrugo Negrete, José Luis | |
dc.contributor.author | Márquez Méndez, Daniela Sofía | |
dc.date.accessioned | 2022-03-30T02:11:21Z | |
dc.date.available | 2023-03-29 | |
dc.date.available | 2022-03-30T02:11:21Z | |
dc.date.issued | 2022-03-29 | |
dc.description.abstract | En este trabajo se analizaron 9 CE en muestras de agua, material suspendido y sedimentos de tres ecosistemas acuáticos del departamento de Córdoba-Colombia, las muestras fueron tomadas en dos temporadas climáticas de lluvia y sequía, el análisis de riesgo se realizó teniendo en cuanta la concentración previa sin efecto y por último el análisis de componentes principales y la distribución se obtuvo mediante la utilización del programa estadístico R studio. Los resultados arrojados en este estudio nos demuestran la presencia de estos CE en dichos ecosistemas además que algunos de ellos en concentraciones que podrían estar afectando al ecosistema. La máxima concentración encontrada en las muestras de agua fue en la bahía de Cispatá en el primer muestreo correspondiente a 15354.15 ng/L de Ibuprofeno, para las muestras de material suspendido fue de 251.69 ng/g de Triclosán detectado en el primer muestreo en la bahía de Cispatá en el caño Zarapa y para los sedimentos la máxima concentración se encontró en Después de playa Blanca con 164.74 ng/g de NPX. En el análisis de componentes principales se determinó una máxima correlación entre los CE del 40.9% en la bahía de Cispatá correspondiente a la componente 1 de dicho análisis. Para el análisis de riesgo ecológico se encontró que en la temporada de lluvia es decir el primer muestreo la bahía de Cispatá en la zona estuarina, la ciénaga de Ayapel en la gran mayoría de sus puntos y la ciénaga de Lorica 3 puntos estaban en riesgo alto. Para el segundo muestreo en la temporada seca la bahía de Cispatá disminuyo el riesgo a casi nulo en todos los puntos, la ciénaga de Ayapel el riesgo se mantuvo alto para todos los puntos y para la ciénaga de Lorica fue alto en tres puntos de muestreo. | spa |
dc.description.abstract | In this work, 9 CE were analyzed in samples of water, suspended material and sediments from three aquatic ecosystems of the department of Córdoba-Colombia, the samples were taken in two climatic seasons of rain and drought, the risk analysis was carried out taking into account the previous concentration without effect and finally the analysis of principal components and the distribution was obtained by using the statistical program R studio. The results obtained in this study show us the presence of these ECs in these ecosystems as well as some of them in concentrations that could be affecting the ecosystem. The maximum concentration found in the water samples was in the Cispatá bay in the first sampling corresponding to 15354.15 ng / L of Ibuprofen, for the suspended material samples it was 251.69 ng / g of Triclosan detected in the first sampling in the bay. of Cispatá in the Zarapa channel and for the sediments the maximum concentration was found in After Playa Blanca with 164.74 ng / g of NPX. In the analysis of principal components, a maximum correlation between the EC of 40.9% was determined in the Cispatá bay corresponding to component 1 of said analysis. For the ecological risk analysis, it was found that in the rainy season, that is, the first sampling the Cispatá Bay in the estuarine zone, the Ayapel swamp in the vast majority of its points and the Lorica swamp 3 points were at high risk | eng |
dc.description.degreelevel | Maestría | spa |
dc.description.degreename | Magíster en Ciencias Ambientales | spa |
dc.description.modality | Trabajos de Investigación y/o Extensión | spa |
dc.description.tableofcontents | RESUMEN................................................................................ 13 | spa |
dc.description.tableofcontents | INTRODUCCIÓN 11.....................................................................................11 | spa |
dc.description.tableofcontents | OBJETIVOS..............................................................................................13 | spa |
dc.description.tableofcontents | OBJETIVO GENERAL..............................................................................13 | spa |
dc.description.tableofcontents | 2.2 OBJETIVOS ESPECÍFICOS...................................................... 13 | spa |
dc.description.tableofcontents | ANTECEDENTES Y MARCO TEORICO................................... 14 | spa |
dc.description.tableofcontents | ANTECEDENTES........................................................................ 14 | spa |
dc.description.tableofcontents | 3.2. MARCO TEORICO......................................................................... 18 | spa |
dc.description.tableofcontents | 3.2.1 Contaminantes emergentes...............................................................18 | spa |
dc.description.tableofcontents | 3.2.2. Contaminación de aguas superficiales por contaminantes emergentes.....23 | spa |
dc.description.tableofcontents | 3.2.3. Contaminación de sedimentos por emergentes....................24 | spa |
dc.description.tableofcontents | 3.2.4. Contaminantes emergentes en solidos suspendidos.......... 24 | spa |
dc.description.tableofcontents | 3.2.5. Vías de entrada de los CE a los ecosistemas acuáticos................25 | spa |
dc.description.tableofcontents | 3.3.5. Normativa de los CE................................................. 27 | spa |
dc.description.tableofcontents | 3.3.6. Métodos de Extracción, detección y cuantificación..............28 | spa |
dc.description.tableofcontents | 4. METODOLOGÍA............................................................ 33 | spa |
dc.description.tableofcontents | 4.1. ÁREAS DE ESTUDIO......................................................... 33 | spa |
dc.description.tableofcontents | 4.1.1 Zona estuarina bahía de Cispatá.......................... 33 | spa |
dc.description.tableofcontents | 4.1.2 Ciénaga De Ayapel......................................... 33 | spa |
dc.description.tableofcontents | 4.1.3 Ciénaga De Lorica............................................................. 34 | spa |
dc.description.tableofcontents | 4.2. TOMA DE MUESTRAS..................................................... 35 | spa |
dc.description.tableofcontents | 4.2.1. Recolección de muestras de agua y sedimento......................36 | spa |
dc.description.tableofcontents | 4.3 ANÁLISIS Y EXTRACCIÓN DE LAS MUESTRAS PARA EL ANALISIS DE CE...........37 | spa |
dc.description.tableofcontents | 4.3.1. Aguas......................................................................................37 | spa |
dc.description.tableofcontents | 4.3.2. Sedimentos....................................................................37 | spa |
dc.description.tableofcontents | 4.3.3. Solidos suspendidos........................................38 | spa |
dc.description.tableofcontents | 4.3.4 Control de calidad analítica.............................................38 | spa |
dc.description.tableofcontents | 4.3.5. Condiciones cromatográficas............................................38 | spa |
dc.description.tableofcontents | 4.4. ANALISIS DE RIESGO ECOLOGICO......................................39 | spa |
dc.description.tableofcontents | 4.5. ANÁLISIS ESTADÍSTICO...................................................41 | spa |
dc.description.tableofcontents | 4.6. DISTRIBUCIÓN DE LOS CONTAMINANTES..................... 41 | spa |
dc.description.tableofcontents | 5. RESULTADOS................................................................. 42 | spa |
dc.description.tableofcontents | 5.1. ANALISIS Y RESULTADOS DE LOS CE EN LAS MATRICES DE ESTUDIO.......42 | spa |
dc.description.tableofcontents | 5.1.1 Contaminantes emergentes en la bahía de Cispatá............ 42 | spa |
dc.description.tableofcontents | 5.1.2 Ayapel....................................................................... 51 | spa |
dc.description.tableofcontents | 5.1.3 Lorica.................................................57 | spa |
dc.description.tableofcontents | 5.2. ANALISIS DE CORRELACIÓN...................... 63 | spa |
dc.description.tableofcontents | 5.2.1 Aguas......................................................................... 63 | spa |
dc.description.tableofcontents | 5.2.2 Sedimentos................................................................66 | spa |
dc.description.tableofcontents | 5.3. COEFICIENTES DE RIESGO EN AGUAS........................70 | spa |
dc.description.tableofcontents | 5.4. DISTRIBUCIÓN ESPACIAL DE LOS COMPUESTOS........... 73 | spa |
dc.description.tableofcontents | 6. CONCLUSIONES.........................................................................94 | spa |
dc.description.tableofcontents | 7. RECOMENDACIONES...................................................96 | spa |
dc.description.tableofcontents | 8. REFERENCIAS BIBLIÓGRAFICAS.............................97 | spa |
dc.format.mimetype | application/pdf | spa |
dc.identifier.uri | https://repositorio.unicordoba.edu.co/handle/ucordoba/5098 | |
dc.language.iso | spa | spa |
dc.publisher | Universidad de Córdoba | |
dc.publisher.faculty | Facultad de Ingeniería | spa |
dc.publisher.place | Montería, Córdoba, Colombia | spa |
dc.publisher.program | Maestría en Ciencias Ambientales | spa |
dc.rights | Copyright Universidad de Córdoba, 2022 | spa |
dc.rights.accessrights | info:eu-repo/semantics/embargoedAccess | spa |
dc.rights.creativecommons | Atribución-NoComercial-SinDerivadas 4.0 Internacional (CC BY-NC-ND 4.0) | spa |
dc.rights.uri | https://creativecommons.org/licenses/by-nc-nd/4.0/ | spa |
dc.subject.keywords | Estuary | eng |
dc.subject.keywords | Swamp | eng |
dc.subject.keywords | Ddrugs | eng |
dc.subject.keywords | Hormones | eng |
dc.subject.keywords | Lipid regulators | eng |
dc.subject.keywords | Chromatography | eng |
dc.subject.keywords | ecological risk | eng |
dc.subject.proposal | Estuario | spa |
dc.subject.proposal | Ciénaga | spa |
dc.subject.proposal | Fármacos | spa |
dc.subject.proposal | Hormonas | spa |
dc.subject.proposal | Regulador de lípidos | spa |
dc.subject.proposal | Cromatografía | spa |
dc.subject.proposal | Riesgo ecológico | spa |
dc.title | Contaminantes emergentes (productos farmacéuticos y de cuidado personal) en aguas y sedimentos de ecosistemas acuáticos del departamento de Córdoba-Colombia | spa |
dc.type | Trabajo de grado - Maestría | spa |
dc.type.coar | http://purl.org/coar/resource_type/c_bdcc | spa |
dc.type.content | Text | spa |
dc.type.driver | info:eu-repo/semantics/masterThesis | spa |
dc.type.redcol | https://purl.org/redcol/resource_type/TM | |
dc.type.version | info:eu-repo/semantics/submittedVersion | spa |
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dspace.entity.type | Publication | |
oaire.accessrights | http://purl.org/coar/access_right/c_f1cf | spa |
oaire.version | http://purl.org/coar/version/c_ab4af688f83e57aa | spa |
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